"OBJECTID"	"ElementID"	"RE"	"RE1"	"RE2"	"RE3"	"RE4"	"RE5"	"PERCENT_"	"PC1"	"PC2"	"PC3"	"PC4"	"PC5"	"RE_LABEL"	"PC_LABEL"	"LANDZONE"	"BD_STATUS"	"BD_SYMBOL"	"VM_CLASS"	"VM_SYMBOL"	"VM_POLY"	"VERSION"	"SCALE"	"L"	"V"	"BVG1M"	"BVG1M_PC"	"DBVG1M"	"DBVG2M"	"DBVG5M"	"Shape_Leng"	"Name"	"re_id"	"re_key"	"vma_class"	"biodivstat"	"biodivstat_notes"	"est_ext"	"ext_res"	"description"	"short_desc"	"short_desc_reg"	"supp_desc"	"subregion"	"protareas"	"special_values"	"Fire_guidelines"	"comments"	"wtqwha"	"bioregion_id"	"landzone_id"	"wetland"	"Structure_category"	"Structure"	"bvg_1m"
1	"Qld_RE_DomE_12.1.1_15825"	"12.1.1"	"12.1.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.1.1"	"100"	"1"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"28a"	"100"	"28a"	"28"	"12"	0.02	"RE_12.1.1"	"12.1.1"	120101.00	"Of concern"	"Endangered"	"under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Casuarina glauca +/- mangroves woodland. Occurs on margins of Quaternary estuarine deposits. (BVG1M: 28a)"	"Casuarina glauca woodland on margins of marine clay plains"	"Casuarina glauca woodland on margins of marine clay plains"	"Ryan, T.S. (ed.) (2012)"	"4, 8, 10, 9"	"Southern Moreton Bay Islands NP, Great Sandy CP, Bribie Island NP, Great Sandy NP, Burrum Coast NP, Eurimbula NP, Pumicestone NP, Curtis Island CP, Eurimbula RR, Eudlo Creek CP, Coombabah Lake CP, Naree Budjong Djara NP (IJMA), Coolum Creek CP, Wild Cattle Island NP, Poona NP, Mouth of Kolan River CP, Mouth of Baffle Creek CP 1, Tallebudgera Creek CP, Curtis Island NP, Noosa NP, Mooloolah River NP, Goat Island (Noosa River) CP, South Stradbroke Island CP, Ningi Creek CP, Bottle Creek CP, Bullock Creek CP, Sheep Island CP, [Deception Bay CP], [Saltwater Creek CP], [Weyba Creek CP], [Hays Inlet CP 1], [Broadwater CP], [Maroochy River CP], [Hays Inlet CP 2], [Fleays Wildlife Park CP], [Maroochy Wetlands CP], [Southend CP], [Fleays CP]"	"Provides estuarine wetland habitat."	"SEASON: Early winter or storm burning seasons. INTENSITY: Low to moderate. INTERVAL: Aim for a 6-7 yr minimum threshold at a broad scale planning level. STRATEGY: Aim to retain at least 25-50% unburnt in any given year. This RE needs disturbance to maintain structure. Use fire to reduce opportunistic native (Allocasuarina spp.) or weed species dominance. Active fire management is required to reduce the accumulation of a significant dry fuel layer. Burns planned in surrounding REs should account for the disturbance requirements of this fringing vegetation. ISSUES: The fire ecology of this regional ecosystem is poorly known. Monitoring the impact of fire and recovery of the ecosystem's component species is highly desirable. A long fire interval could increase fire intensity when fire occurs, thus detrimentally affecting the tree layer. Recovery should be relatively quick (~10 years to a woodland/open forest community). A 'grassy' ecosystem might be lost if fire is excluded or too frequent (<2 years). Signs of problems in this community might include the regeneration of 'whipstick' communities and/or the presence of weeds (such as lantana). Fire exclusion and buffering from fire is not necessary. Where obligate seeding allocasuarinas are present in the under- and mid-storeys, fires causing 100% leaf scorch will kill these trees; therefore fires of this intensity should be avoided. A seven year minimum fire interval is required for obligate seeding allocasuarinas and casuarinas."	"Subject to weed invasion, especially groundsel (Baccharis halimifolia). Patches often too small to map at 1:100 000."		12.00	1.00	"Estuarine wetlands (e.g. mangroves)."	"Sparse"	"W"	"28a"
2	"Qld_RE_DomE_12.1.1_16239"	"12.1.1"	"12.1.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.1.1"	"100"	"1"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"28a"	"100"	"28a"	"28"	"12"	9.11989216736e-03	"RE_12.1.1"	"12.1.1"	120101.00	"Of concern"	"Endangered"	"under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Casuarina glauca +/- mangroves woodland. Occurs on margins of Quaternary estuarine deposits. (BVG1M: 28a)"	"Casuarina glauca woodland on margins of marine clay plains"	"Casuarina glauca woodland on margins of marine clay plains"	"Ryan, T.S. (ed.) (2012)"	"4, 8, 10, 9"	"Southern Moreton Bay Islands NP, Great Sandy CP, Bribie Island NP, Great Sandy NP, Burrum Coast NP, Eurimbula NP, Pumicestone NP, Curtis Island CP, Eurimbula RR, Eudlo Creek CP, Coombabah Lake CP, Naree Budjong Djara NP (IJMA), Coolum Creek CP, Wild Cattle Island NP, Poona NP, Mouth of Kolan River CP, Mouth of Baffle Creek CP 1, Tallebudgera Creek CP, Curtis Island NP, Noosa NP, Mooloolah River NP, Goat Island (Noosa River) CP, South Stradbroke Island CP, Ningi Creek CP, Bottle Creek CP, Bullock Creek CP, Sheep Island CP, [Deception Bay CP], [Saltwater Creek CP], [Weyba Creek CP], [Hays Inlet CP 1], [Broadwater CP], [Maroochy River CP], [Hays Inlet CP 2], [Fleays Wildlife Park CP], [Maroochy Wetlands CP], [Southend CP], [Fleays CP]"	"Provides estuarine wetland habitat."	"SEASON: Early winter or storm burning seasons. INTENSITY: Low to moderate. INTERVAL: Aim for a 6-7 yr minimum threshold at a broad scale planning level. STRATEGY: Aim to retain at least 25-50% unburnt in any given year. This RE needs disturbance to maintain structure. Use fire to reduce opportunistic native (Allocasuarina spp.) or weed species dominance. Active fire management is required to reduce the accumulation of a significant dry fuel layer. Burns planned in surrounding REs should account for the disturbance requirements of this fringing vegetation. ISSUES: The fire ecology of this regional ecosystem is poorly known. Monitoring the impact of fire and recovery of the ecosystem's component species is highly desirable. A long fire interval could increase fire intensity when fire occurs, thus detrimentally affecting the tree layer. Recovery should be relatively quick (~10 years to a woodland/open forest community). A 'grassy' ecosystem might be lost if fire is excluded or too frequent (<2 years). Signs of problems in this community might include the regeneration of 'whipstick' communities and/or the presence of weeds (such as lantana). Fire exclusion and buffering from fire is not necessary. Where obligate seeding allocasuarinas are present in the under- and mid-storeys, fires causing 100% leaf scorch will kill these trees; therefore fires of this intensity should be avoided. A seven year minimum fire interval is required for obligate seeding allocasuarinas and casuarinas."	"Subject to weed invasion, especially groundsel (Baccharis halimifolia). Patches often too small to map at 1:100 000."		12.00	1.00	"Estuarine wetlands (e.g. mangroves)."	"Sparse"	"W"	"28a"
3	"Qld_RE_DomE_12.11.23_16288"	"12.11.23/12.11.5j"	"12.11.23"	"12.11.5j"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.11.23/12.11.5"	"90/10"	"11"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"8b/9a"	"90/10"	"8b"	"8"	"2"	2.83787066818e-03	"RE_12.11.23/12.11.5j"	"12.11.23"	121123.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Eucalyptus pilularis open forest. Other canopy species include E. microcorys, Corymbia intermedia, Angophora woodsiana, E. tindaliae and E. carnea. E. racemosa subsp. racemosa and Corymbia trachyphloia are prominent in the Venman area whilst C. gummifera and E. resinifera are prominent in the Nerang area. Occurs on low coastal Palaeozoic and older moderately to strongly deformed and metamorphosed sediments and interbedded volcanics (Neranleigh-Fernvale beds). (BVG1M: 8b)"	"Eucalyptus pilularis open forest on coastal metamorphics and interbedded volcanics"	"Eucalyptus pilularis open forest on coastal metamorphics and interbedded volcanics"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998) H39f, H39g"	"3, 4"	"Venman Bushland NP, Bayview CP, Carbrook Wetlands CP 2, Carbrook Wetlands CP 1, Burleigh Knoll CP"		"SEASON: Summer to winter. INTENSITY: Plan for low to moderate. Unplanned occasional high intensity wildfire will occur. INTERVAL: 4-8 years maintains a healthy grassy system. 8-20 years for shrubby elements of understorey. STRATEGY: Aim for 40-60% mosaic burn. Needs disturbance to maintain RE structure (eucalypt overstorey with open understorey of predominantly non-rainforest species). ISSUES: Frequent fire is needed to maintain understorey integrity, keeping more mesic species low in the profile of the understorey so that other species can compete. However, rainforest invasion is only a problem in moister forest south of the Logan River. North of the Logan River around Venman Reserve this RE occurs at higher elevation and is drier. Burning regimes will need to be adjusted according to location. High fuel loads develop within a short period of time owing to bark drop. High intensity fires occur periodically through time, however frequent low to moderate intensity fires will create the disturbance required to keep the understorey diverse. A follow-up burn soon after a high intensity wildfire can be considered to reduce germinating mesic species. This 'endangered' RE may contain a high number of rare and threatened plant species which require appropriate fire management."	"Restricted to coastal metasediments (Neranleigh-Fernvale beds) from Logan south to the border. Extensively cleared and fragmented by urban development."		12.00	11.00		"Mid-dense"	"OF"	"8b"
4	"Qld_RE_DomE_12.11.23_16290"	"12.11.23/12.11.5j"	"12.11.23"	"12.11.5j"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.11.23/12.11.5"	"90/10"	"11"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"8b/9a"	"90/10"	"8b"	"8"	"2"	6.18632919696e-03	"RE_12.11.23/12.11.5j"	"12.11.23"	121123.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Eucalyptus pilularis open forest. Other canopy species include E. microcorys, Corymbia intermedia, Angophora woodsiana, E. tindaliae and E. carnea. E. racemosa subsp. racemosa and Corymbia trachyphloia are prominent in the Venman area whilst C. gummifera and E. resinifera are prominent in the Nerang area. Occurs on low coastal Palaeozoic and older moderately to strongly deformed and metamorphosed sediments and interbedded volcanics (Neranleigh-Fernvale beds). (BVG1M: 8b)"	"Eucalyptus pilularis open forest on coastal metamorphics and interbedded volcanics"	"Eucalyptus pilularis open forest on coastal metamorphics and interbedded volcanics"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998) H39f, H39g"	"3, 4"	"Venman Bushland NP, Bayview CP, Carbrook Wetlands CP 2, Carbrook Wetlands CP 1, Burleigh Knoll CP"		"SEASON: Summer to winter. INTENSITY: Plan for low to moderate. Unplanned occasional high intensity wildfire will occur. INTERVAL: 4-8 years maintains a healthy grassy system. 8-20 years for shrubby elements of understorey. STRATEGY: Aim for 40-60% mosaic burn. Needs disturbance to maintain RE structure (eucalypt overstorey with open understorey of predominantly non-rainforest species). ISSUES: Frequent fire is needed to maintain understorey integrity, keeping more mesic species low in the profile of the understorey so that other species can compete. However, rainforest invasion is only a problem in moister forest south of the Logan River. North of the Logan River around Venman Reserve this RE occurs at higher elevation and is drier. Burning regimes will need to be adjusted according to location. High fuel loads develop within a short period of time owing to bark drop. High intensity fires occur periodically through time, however frequent low to moderate intensity fires will create the disturbance required to keep the understorey diverse. A follow-up burn soon after a high intensity wildfire can be considered to reduce germinating mesic species. This 'endangered' RE may contain a high number of rare and threatened plant species which require appropriate fire management."	"Restricted to coastal metasediments (Neranleigh-Fernvale beds) from Logan south to the border. Extensively cleared and fragmented by urban development."		12.00	11.00		"Mid-dense"	"OF"	"8b"
5	"Qld_RE_DomE_12.11.23_16340"	"12.11.23/12.11.5j"	"12.11.23"	"12.11.5j"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.11.23/12.11.5"	"90/10"	"11"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"8b/9a"	"90/10"	"8b"	"8"	"2"	0.01	"RE_12.11.23/12.11.5j"	"12.11.23"	121123.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Eucalyptus pilularis open forest. Other canopy species include E. microcorys, Corymbia intermedia, Angophora woodsiana, E. tindaliae and E. carnea. E. racemosa subsp. racemosa and Corymbia trachyphloia are prominent in the Venman area whilst C. gummifera and E. resinifera are prominent in the Nerang area. Occurs on low coastal Palaeozoic and older moderately to strongly deformed and metamorphosed sediments and interbedded volcanics (Neranleigh-Fernvale beds). (BVG1M: 8b)"	"Eucalyptus pilularis open forest on coastal metamorphics and interbedded volcanics"	"Eucalyptus pilularis open forest on coastal metamorphics and interbedded volcanics"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998) H39f, H39g"	"3, 4"	"Venman Bushland NP, Bayview CP, Carbrook Wetlands CP 2, Carbrook Wetlands CP 1, Burleigh Knoll CP"		"SEASON: Summer to winter. INTENSITY: Plan for low to moderate. Unplanned occasional high intensity wildfire will occur. INTERVAL: 4-8 years maintains a healthy grassy system. 8-20 years for shrubby elements of understorey. STRATEGY: Aim for 40-60% mosaic burn. Needs disturbance to maintain RE structure (eucalypt overstorey with open understorey of predominantly non-rainforest species). ISSUES: Frequent fire is needed to maintain understorey integrity, keeping more mesic species low in the profile of the understorey so that other species can compete. However, rainforest invasion is only a problem in moister forest south of the Logan River. North of the Logan River around Venman Reserve this RE occurs at higher elevation and is drier. Burning regimes will need to be adjusted according to location. High fuel loads develop within a short period of time owing to bark drop. High intensity fires occur periodically through time, however frequent low to moderate intensity fires will create the disturbance required to keep the understorey diverse. A follow-up burn soon after a high intensity wildfire can be considered to reduce germinating mesic species. This 'endangered' RE may contain a high number of rare and threatened plant species which require appropriate fire management."	"Restricted to coastal metasediments (Neranleigh-Fernvale beds) from Logan south to the border. Extensively cleared and fragmented by urban development."		12.00	11.00		"Mid-dense"	"OF"	"8b"
6	"Qld_RE_DomE_12.3.1_15905"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	7.84819438488e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
7	"Qld_RE_DomE_12.3.1_15906"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	7.03149874223e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
8	"Qld_RE_DomE_12.3.1_15907"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	8.62490156416e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
9	"Qld_RE_DomE_12.3.1_15914"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	6.91119711883e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
10	"Qld_RE_DomE_12.3.1_15926"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	0.01	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
11	"Qld_RE_DomE_12.3.1_15936"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	5.14159562573e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
12	"Qld_RE_DomE_12.3.1_15937"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	8.20317650719e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
13	"Qld_RE_DomE_12.3.1_15944"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	3.1590655715e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
14	"Qld_RE_DomE_12.3.1_15954"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	4.7479200852e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
15	"Qld_RE_DomE_12.3.1_15958"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	4.25580876018e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
16	"Qld_RE_DomE_12.3.1_15961"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	4.27056707362e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
17	"Qld_RE_DomE_12.3.1_15967"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	5.43350067382e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
18	"Qld_RE_DomE_12.3.1_15973"	"12.3.1/12.3.11"	"12.3.1"	"12.3.11"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.11"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b/16c"	"90/10"	"4b"	"4"	"1"	5.02045130962e-03	"RE_12.3.1/12.3.11"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
19	"Qld_RE_DomE_12.3.1_16587"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b"	"100"	"4b"	"4"	"1"	0.01	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
20	"Qld_RE_DomE_12.3.1_16617"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b"	"100"	"4b"	"4"	"1"	2.0804804075e-03	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
21	"Qld_RE_DomE_12.3.1_16622"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b"	"100"	"4b"	"4"	"1"	3.42174070516e-03	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
22	"Qld_RE_DomE_12.3.1_16635"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b"	"100"	"4b"	"4"	"1"	5.63839630332e-03	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
23	"Qld_RE_DomE_12.3.1_16640"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b"	"100"	"4b"	"4"	"1"	5.87262866949e-03	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
24	"Qld_RE_DomE_12.3.1_16649"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"4b"	"100"	"4b"	"4"	"1"	3.4107683642e-03	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
25	"Qld_RE_DomE_12.3.1_18254"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b"	"100"	"4b"	"4"	"1"	3.92013022983e-03	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
26	"Qld_RE_DomE_12.3.1_18575"	"12.3.1/12.3.7"	"12.3.1"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b/16a"	"90/10"	"4b"	"4"	"1"	0.05	"RE_12.3.1/12.3.7"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
27	"Qld_RE_DomE_12.3.1_18608"	"12.3.1/12.3.7"	"12.3.1"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b/16a"	"90/10"	"4b"	"4"	"1"	0.03	"RE_12.3.1/12.3.7"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
28	"Qld_RE_DomE_12.3.1_18625"	"12.3.1/12.3.7"	"12.3.1"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b/16a"	"90/10"	"4b"	"4"	"1"	0.01	"RE_12.3.1/12.3.7"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
29	"Qld_RE_DomE_12.3.1_18630"	"12.3.1/12.3.7"	"12.3.1"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b/16a"	"90/10"	"4b"	"4"	"1"	0.02	"RE_12.3.1/12.3.7"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
30	"Qld_RE_DomE_12.3.1_18663"	"12.3.1/12.3.7"	"12.3.1"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b/16a"	"90/10"	"4b"	"4"	"1"	5.4609570726e-03	"RE_12.3.1/12.3.7"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
31	"Qld_RE_DomE_12.3.1_18702"	"12.3.1/12.3.7"	"12.3.1"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.1/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b/16a"	"90/10"	"4b"	"4"	"1"	0.01	"RE_12.3.1/12.3.7"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
32	"Qld_RE_DomE_12.3.1_18811"	"12.3.1/12.3.7"	"12.3.1"	"12.3.7"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.3.1/12.3.7"	"80/20"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b/16a"	"80/20"	"4b"	"4"	"1"	0.01	"RE_12.3.1/12.3.7"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
33	"Qld_RE_DomE_12.3.1_19033"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"4b"	"100"	"4b"	"4"	"1"	0.02	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
34	"Qld_RE_DomE_12.3.1_19138"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"4b"	"100"	"4b"	"4"	"1"	9.59591227452e-03	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
35	"Qld_RE_DomE_12.3.1_19311"	"12.3.1"	"12.3.1"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.1"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"4b"	"100"	"4b"	"4"	"1"	0.02	"RE_12.3.1"	"12.3.1"	120301.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Complex to simple notophyll vine forest. Waterhousea floribunda is predominant fringing stream channels. Other species can include Cryptocarya hypospodia, C. obovata, C. triplinervis, Argyrodendron trifoliolatum, Ficus coronata, F. fraseri, F. macrophylla forma macrophylla, Aphananthe philippinensis, Elaeocarpus grandis, Grevillea robusta, Castanospermum australe and Syzygium francisii. Ficus racemosa and Nauclea orientalis in north of bioregion. Eucalyptus spp. emergents (e.g. E. grandis) and Araucaria cunninghamii; less commonly Agathis robusta may also be present. Occurs on Quaternary alluvial plains and channels. (BVG1M: 4b)"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Gallery rainforest (notophyll vine forest) on alluvial plains"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E1, E3-5"	"3, 7, 8, 4, 2, 10, (9), (6), (1)"	"Wongi NP, Bulburin NP, Eurimbula NP, Conondale NP, Tewantin NP, Great Sandy NP, D'Aguilar NP, Kondalilla NP, Mooloolah River NP, Goomboorian NP, Mapleton NP, Eumundi CP, Dularcha NP, Woondum NP, Ferntree Creek NP, Lamington NP, Mount Binga NP, Springbrook NP, Palmview CP, Tuchekoi NP, Mapleton NP (R), Mount Cooroy CP, Meridan Plains CP, Baffle Creek CP, Venman Bushland NP, Fairlies Knob NP, [Dawes NP (R)], [Woondum CP], [Woowoonga NP], [Kroombit Tops NP], [Six Mile Creek CP], [Neurum Creek CP], [Mapleton CP], [Bribie Island NP], [Maleny NP], [Goomboorian NP (R)], [Sarabah NP]"	"Habitat for threatened flora species including Xanthostemon oppositifolius, Fontainea rostrata, Macadamia integrifolia and M. ternifolia. Habitat for threatened fauna species including Cyclopsitta diophthalma coxeni and Ornithoptera richmondia. Important for fruit-eating birds, many of which migrate seasonally from upland to lowland rainforest."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Occurs up to about 100 km inland. Extensively cleared for agriculture. Prone to invasion by weeds such as camphor laurel Cinnamomum camphora, broad leaved pepper tree Schinus terebinthifolius, cat's claw creeper Macfadyena unguis-cati on margins and when disturbed. Often too narrow to be mapped at 1:100 000 scale. The types recognised by Bean et al. (1998) indicate that geographical patterns are evident within the RE."		12.00	3.00	"Riverine wetland or fringing riverine wetland."	"Dense"	"CF"	"4b"
36	"Qld_RE_DomE_12.3.10a_16449"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	5.06421256386e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
37	"Qld_RE_DomE_12.3.10a_16453"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	2.56741197156e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
38	"Qld_RE_DomE_12.3.10a_16454"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	5.19374399586e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
39	"Qld_RE_DomE_12.3.10a_16534"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	8.77310482184e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
40	"Qld_RE_DomE_12.3.10a_16542"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	4.83515755263e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
41	"Qld_RE_DomE_12.3.10a_16551"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	6.90460610088e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
42	"Qld_RE_DomE_12.3.10a_16868"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	6.11126766419e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
43	"Qld_RE_DomE_12.3.10a_16887"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	3.49277364293e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
44	"Qld_RE_DomE_12.3.10a_16899"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	7.45201904123e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
45	"Qld_RE_DomE_12.3.10a_17106"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	8.00841105512e-03	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
46	"Qld_RE_DomE_12.3.10a_17285"	"12.3.10a"	"12.3.10a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.10"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"25a"	"100"	"25a"	"25"	"10"	0.01	"RE_12.3.10a"	"12.3.10"	120310.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Eucalyptus populnea +/- E. tereticornis grassy woodland/tall woodland +/- patches of Acacia harpophylla and Melaleuca bracteata. Occurs on Quaternary alluvial plains. (BVG1M: 17a)
 Vegetation communities in this regional ecosystem include: 
12.3.10a:  Acacia harpophylla open forest to woodland. Occurs on Quaternary alluvial plains where minor areas of cracking clay soils prevail. (BVG1M: 25a)"	"Eucalyptus populnea woodland on alluvial plains"	"Eucalyptus populnea woodland on alluvial plains"	"Bean et al. (1998), E8"	"5, 2, 10, 6, (7)"	"No representation"		"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.10: Confined to western margins of bioregion. Cleared and thinned for grazing and agriculture. Some relatively intact remnants present in road reserves. Eucalyptus populnea is one of the species characteristics of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions.
12.3.10a: Confined to Lockyer Valley. Cleared and thinned for grazing and agriculture. Acacia harpophylla is one of the species characteristic of the broad overlap between the Southeast Queensland and Brigalow Belt bioregions."		12.00	3.00	"Contains palustrine wetland (e.g. in swales)."	"Sparse"	"W"	"17a"
47	"Qld_RE_DomE_12.3.3_16045"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
48	"Qld_RE_DomE_12.3.3_16095"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
49	"Qld_RE_DomE_12.3.3_16097"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	8.12292724958e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
50	"Qld_RE_DomE_12.3.3_16119"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.33071171223e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
51	"Qld_RE_DomE_12.3.3_16156"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	2.32091840568e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
52	"Qld_RE_DomE_12.3.3_16292"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
53	"Qld_RE_DomE_12.3.3_16301"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	7.23394881879e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
54	"Qld_RE_DomE_12.3.3_16325"	"12.3.3/12.3.3a/12.3.3d"	"12.3.3"	"12.3.3a"	"12.3.3d"	" "	" "	"60/30/10"	60	30	10	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/18b/13d"	"60/30/10"	"16c"	"16"	"4"	0.05	"RE_12.3.3/12.3.3a/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
132	"Qld_RE_DomE_12.3.3_17701"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
133	"Qld_RE_DomE_12.3.3_17719"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.08	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
134	"Qld_RE_DomE_12.3.3_17720"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	9.38433807257e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
135	"Qld_RE_DomE_12.3.3_17730"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.84509140035e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
136	"Qld_RE_DomE_12.3.3_17738"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.07	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
271	"Qld_RE_DomE_12.3.3_18915"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.14300582345e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
272	"Qld_RE_DomE_12.3.3_18923"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
273	"Qld_RE_DomE_12.3.3_18970"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	9.5096825249e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
274	"Qld_RE_DomE_12.3.3_18993"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.07	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
275	"Qld_RE_DomE_12.3.3_19001"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
578	"Qld_RE_DomE_12.5.3a_16332"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.59247996667e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
579	"Qld_RE_DomE_12.5.3a_16334"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
580	"Qld_RE_DomE_12.5.3a_16343"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
581	"Qld_RE_DomE_12.5.3a_16353"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.12412242631e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
582	"Qld_RE_DomE_12.5.3a_16354"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.21165739022e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
583	"Qld_RE_DomE_12.5.3a_16356"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	2.26365726169e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
538	"Qld_RE_DomE_12.5.3a_16146"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	8.70212037712e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
539	"Qld_RE_DomE_12.5.3a_16147"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	6.38553311658e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
540	"Qld_RE_DomE_12.5.3a_16153"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.39467256945e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
541	"Qld_RE_DomE_12.5.3a_16163"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.29905558514e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
542	"Qld_RE_DomE_12.5.3a_16165"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.755994734e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
732	"Qld_RE_DomE_12.8.24_19494"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.07	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
733	"Qld_RE_DomE_12.8.24_19496"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
734	"Qld_RE_DomE_12.8.24_19524"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.04	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
735	"Qld_RE_DomE_12.8.24_19535"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.09	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
736	"Qld_RE_DomE_12.8.24_19542"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
1006	"Qld_RE_DomE_12.9-10.12_17279"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.06	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1007	"Qld_RE_DomE_12.9-10.12_17282"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1008	"Qld_RE_DomE_12.9-10.12_17287"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	5.69231108563e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1009	"Qld_RE_DomE_12.9-10.12_17292"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1010	"Qld_RE_DomE_12.9-10.12_17300"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.27106241613e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1142	"Qld_RE_DomE_12.9-10.12_18095"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.89408838984e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1143	"Qld_RE_DomE_12.9-10.12_18096"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.7"	"60/40"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/12a"	"60/40"	"9a"	"9"	"3"	3.72377947856e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1144	"Qld_RE_DomE_12.9-10.12_18097"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.50515642448e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1145	"Qld_RE_DomE_12.9-10.12_18103"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.66348310572e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1146	"Qld_RE_DomE_12.9-10.15_16576"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"7a"	"100"	"7a"	"7"	"1"	4.15461509021e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1282	"Qld_RE_DomE_12.9-10.6_18242"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	0.01	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1283	"Qld_RE_DomE_12.9-10.6_18269"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.08333283923e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1284	"Qld_RE_DomE_12.9-10.6_18272"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	6.30918874241e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1285	"Qld_RE_DomE_12.9-10.6_18276"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	5.42279854256e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1286	"Qld_RE_DomE_12.9-10.6_18281"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	5.94746893759e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
321	"Qld_RE_DomE_12.3.3b_16842"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	6.54972101861e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
322	"Qld_RE_DomE_12.3.3b_16845"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.92683471555e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
323	"Qld_RE_DomE_12.3.3b_16849"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	7.91153853499e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
324	"Qld_RE_DomE_12.3.3b_16854"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	8.57462509898e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
325	"Qld_RE_DomE_12.3.3b_16875"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	4.83439776427e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
331	"Qld_RE_DomE_12.3.3b_17013"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
332	"Qld_RE_DomE_12.3.3b_17056"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	8.30653370549e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
333	"Qld_RE_DomE_12.3.3b_17066"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
334	"Qld_RE_DomE_12.3.3b_17076"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
335	"Qld_RE_DomE_12.3.3b_17101"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
721	"Qld_RE_DomE_12.8.24_19433"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.05	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
722	"Qld_RE_DomE_12.8.24_19434"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
723	"Qld_RE_DomE_12.8.24_19445"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	9.49402316224e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
724	"Qld_RE_DomE_12.8.24_19462"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
725	"Qld_RE_DomE_12.8.24_19465"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
945	"Qld_RE_DomE_12.9-10.12_16932"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.19"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
946	"Qld_RE_DomE_12.9-10.12_16935"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
947	"Qld_RE_DomE_12.9-10.12_16941"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.60938766043e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
948	"Qld_RE_DomE_12.9-10.12_16958"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
949	"Qld_RE_DomE_12.9-10.12_16962"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.96158734539e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
118	"Qld_RE_DomE_12.3.3_17588"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	0.02	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
119	"Qld_RE_DomE_12.3.3_17590"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	0.02	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
120	"Qld_RE_DomE_12.3.3_17596"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	7.28443860194e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
121	"Qld_RE_DomE_12.3.3_17597"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	2.94018621751e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
242	"Qld_RE_DomE_12.3.3_18383"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.07874596093e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
243	"Qld_RE_DomE_12.3.3_18385"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	6.99446463599e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
244	"Qld_RE_DomE_12.3.3_18397"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	2.78856662128e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
245	"Qld_RE_DomE_12.3.3_18404"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	5.83319337075e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
246	"Qld_RE_DomE_12.3.3_18414"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
401	"Qld_RE_DomE_12.3.3c_17007"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.35580236413e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
402	"Qld_RE_DomE_12.3.3c_17011"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.95228747325e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
403	"Qld_RE_DomE_12.3.3c_17041"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.09225005449e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
404	"Qld_RE_DomE_12.3.3c_17047"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	8.84225640031e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
405	"Qld_RE_DomE_12.3.3c_17051"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.1528057176e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
1084	"Qld_RE_DomE_12.9-10.12_17638"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.57619601426e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1085	"Qld_RE_DomE_12.9-10.12_17645"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1086	"Qld_RE_DomE_12.9-10.12_17648"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1087	"Qld_RE_DomE_12.9-10.12_17649"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1088	"Qld_RE_DomE_12.9-10.12_17652"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.0775198243e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1109	"Qld_RE_DomE_12.9-10.12_17700"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.71896883282e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1110	"Qld_RE_DomE_12.9-10.12_17706"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.34678029351e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1111	"Qld_RE_DomE_12.9-10.12_17707"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.88993674935e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1112	"Qld_RE_DomE_12.9-10.12_17710"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1113	"Qld_RE_DomE_12.9-10.12_17715"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.22164441471e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1089	"Qld_RE_DomE_12.9-10.12_17660"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.50153804795e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1090	"Qld_RE_DomE_12.9-10.12_17661"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.92662909813e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1091	"Qld_RE_DomE_12.9-10.12_17662"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.90288183379e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1092	"Qld_RE_DomE_12.9-10.12_17664"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1093	"Qld_RE_DomE_12.9-10.12_17666"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.80864467718e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1147	"Qld_RE_DomE_12.9-10.15_16593"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"7a"	"100"	"7a"	"7"	"1"	7.0947865188e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1148	"Qld_RE_DomE_12.9-10.15_16629"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"7a"	"100"	"7a"	"7"	"1"	7.54863655519e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1149	"Qld_RE_DomE_12.9-10.15_18045"	"12.9-10.15/12.9-10.17"	"12.9-10.15"	"12.9-10.17"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.9-10.15/12.9-10.17"	"95/5"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a/9a"	"95/5"	"7a"	"7"	"1"	0.01	"RE_12.9-10.15/12.9-10.17"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1150	"Qld_RE_DomE_12.9-10.15_18054"	"12.9-10.15/12.9-10.17"	"12.9-10.15"	"12.9-10.17"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.9-10.15/12.9-10.17"	"95/5"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a/9a"	"95/5"	"7a"	"7"	"1"	0.01	"RE_12.9-10.15/12.9-10.17"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1200	"Qld_RE_DomE_12.9-10.16_19173"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.07	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1201	"Qld_RE_DomE_12.9-10.16_19185"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	7.23806433217e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1202	"Qld_RE_DomE_12.9-10.16_19189"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1203	"Qld_RE_DomE_12.9-10.16_19193"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	7.24427075843e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1204	"Qld_RE_DomE_12.9-10.16_19203"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
142	"Qld_RE_DomE_12.3.3_17758"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.04	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
143	"Qld_RE_DomE_12.3.3_17761"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	8.0082682663e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
144	"Qld_RE_DomE_12.3.3_17789"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.10367376683e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
145	"Qld_RE_DomE_12.3.3_17790"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	7.27207317645e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
146	"Qld_RE_DomE_12.3.3_17798"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.06	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
276	"Qld_RE_DomE_12.3.3_19023"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
277	"Qld_RE_DomE_12.3.3_19025"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
278	"Qld_RE_DomE_12.3.3_19087"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.98810711534e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
279	"Qld_RE_DomE_12.3.3_19094"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
280	"Qld_RE_DomE_12.3.3_19096"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
436	"Qld_RE_DomE_12.3.3d_16768"	"12.3.3d/12.3.3"	"12.3.3d"	"12.3.3"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d/16c"	"70/30"	"13d"	"13"	"3"	0.02	"RE_12.3.3d/12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
437	"Qld_RE_DomE_12.3.3d_16804"	"12.3.3d/12.3.3"	"12.3.3d"	"12.3.3"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d/16c"	"70/30"	"13d"	"13"	"3"	9.03000633797e-03	"RE_12.3.3d/12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
438	"Qld_RE_DomE_12.3.3d_16813"	"12.3.3d/12.3.3"	"12.3.3d"	"12.3.3"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d/16c"	"70/30"	"13d"	"13"	"3"	0.01	"RE_12.3.3d/12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
439	"Qld_RE_DomE_12.3.3d_16816"	"12.3.3d/12.3.3"	"12.3.3d"	"12.3.3"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d/16c"	"70/30"	"13d"	"13"	"3"	0.01	"RE_12.3.3d/12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
440	"Qld_RE_DomE_12.3.3d_16843"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
526	"Qld_RE_DomE_12.5.3a_16105"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	2.62639056767e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
527	"Qld_RE_DomE_12.5.3a_16106"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.55923612102e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
528	"Qld_RE_DomE_12.5.3a_16107"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	8.26687988988e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
529	"Qld_RE_DomE_12.5.3a_16113"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
530	"Qld_RE_DomE_12.5.3a_16115"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	8.51792838926e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
547	"Qld_RE_DomE_12.5.3a_16210"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.35545649564e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
548	"Qld_RE_DomE_12.5.3a_16213"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
549	"Qld_RE_DomE_12.5.3a_16215"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.98191540397e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
550	"Qld_RE_DomE_12.5.3a_16216"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.02	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
551	"Qld_RE_DomE_12.5.3a_16225"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.49609808695e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
646	"Qld_RE_DomE_12.8.24_17801"	"12.8.24/12.8.20"	"12.8.24"	"12.8.20"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.8.24/12.8.20"	"95/5"	"8"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b/9a"	"95/5"	"10b"	"10"	"3"	0.02	"RE_12.8.24/12.8.20"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
647	"Qld_RE_DomE_12.8.24_17883"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
648	"Qld_RE_DomE_12.8.24_17895"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	8.22670201193e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
649	"Qld_RE_DomE_12.8.24_17899"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	8.44801468976e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
650	"Qld_RE_DomE_12.8.24_17903"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
686	"Qld_RE_DomE_12.8.24_18780"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	8.36823359766e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
687	"Qld_RE_DomE_12.8.24_18788"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
688	"Qld_RE_DomE_12.8.24_18810"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	4.66391894977e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
689	"Qld_RE_DomE_12.8.24_18815"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.06	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
690	"Qld_RE_DomE_12.8.24_18824"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.06	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
426	"Qld_RE_DomE_12.3.3d_16489"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
427	"Qld_RE_DomE_12.3.3d_16490"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.04	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
428	"Qld_RE_DomE_12.3.3d_16493"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	5.76634946134e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
429	"Qld_RE_DomE_12.3.3d_16535"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	7.20276093991e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
430	"Qld_RE_DomE_12.3.3d_16544"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	3.03451777948e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
501	"Qld_RE_DomE_12.5.3_15939"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
502	"Qld_RE_DomE_12.5.3_16086"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.78212433803e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
503	"Qld_RE_DomE_12.5.3a_15909"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	0.03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
504	"Qld_RE_DomE_12.5.3a_15950"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	9.26255698783e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
505	"Qld_RE_DomE_12.5.3a_15956"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
584	"Qld_RE_DomE_12.5.3a_16358"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	9.64362409414e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
585	"Qld_RE_DomE_12.5.3a_16360"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.06990865637e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
586	"Qld_RE_DomE_12.5.3a_16362"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
587	"Qld_RE_DomE_12.5.3a_16366"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.26746232942e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
588	"Qld_RE_DomE_12.5.3a_16367"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
589	"Qld_RE_DomE_12.5.3a_16371"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	6.49039436481e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
766	"Qld_RE_DomE_12.9-10.11_17286"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.0156918431e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
767	"Qld_RE_DomE_12.9-10.11_17322"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.01958099604e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
768	"Qld_RE_DomE_12.9-10.11_17333"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
769	"Qld_RE_DomE_12.9-10.11_17337"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.68983461191e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
770	"Qld_RE_DomE_12.9-10.11_17381"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
884	"Qld_RE_DomE_12.9-10.12_16355"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	5.278931405e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
885	"Qld_RE_DomE_12.9-10.12_16359"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	2.27820738364e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
886	"Qld_RE_DomE_12.9-10.12_16382"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	9.24724151061e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
887	"Qld_RE_DomE_12.9-10.12_16392"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	9.10778193544e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
55	"Qld_RE_DomE_12.3.3_16347"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.26006710476e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
56	"Qld_RE_DomE_12.3.3_16350"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
57	"Qld_RE_DomE_12.3.3_16368"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
58	"Qld_RE_DomE_12.3.3_16396"	"12.3.3/12.3.7"	"12.3.3"	"12.3.7"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.3.3/12.3.7"	"70/30"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/16a"	"70/30"	"16c"	"16"	"4"	8.9971621875e-03	"RE_12.3.3/12.3.7"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
59	"Qld_RE_DomE_12.3.3_16398"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
60	"Qld_RE_DomE_12.3.3_16400"	"12.3.3/12.9-10.7/12.9-10.3"	"12.3.3"	"12.9-10.7"	"12.9-10.3"	" "	" "	"80/15/5"	80	15	5	0	0	"12.3.3/12.9-10.7/12.9-10.3"	"80/15/5"	"3"	"E/OC/OC"	254	"E/O/O"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13c/13d"	"80/15/5"	"16c"	"16"	"4"	5.45384583899e-03	"RE_12.3.3/12.9-10.7/12.9-10.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
61	"Qld_RE_DomE_12.3.3_16404"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
62	"Qld_RE_DomE_12.3.3_16410"	"12.3.3/12.9-10.7/12.9-10.3"	"12.3.3"	"12.9-10.7"	"12.9-10.3"	" "	" "	"80/15/5"	80	15	5	0	0	"12.3.3/12.9-10.7/12.9-10.3"	"80/15/5"	"3"	"E/OC/OC"	254	"E/O/O"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13c/13d"	"80/15/5"	"16c"	"16"	"4"	0.02	"RE_12.3.3/12.9-10.7/12.9-10.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
63	"Qld_RE_DomE_12.3.3_16422"	"12.3.3/12.3.3a/12.3.3d"	"12.3.3"	"12.3.3a"	"12.3.3d"	" "	" "	"60/30/10"	60	30	10	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/18b/13d"	"60/30/10"	"16c"	"16"	"4"	0.01	"RE_12.3.3/12.3.3a/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
64	"Qld_RE_DomE_12.3.3_16447"	"12.3.3/12.9-10.7/12.9-10.3"	"12.3.3"	"12.9-10.7"	"12.9-10.3"	" "	" "	"60/30/10"	60	30	10	0	0	"12.3.3/12.9-10.7/12.9-10.3"	"60/30/10"	"3"	"E/OC/OC"	254	"E/O/O"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13c/13d"	"60/30/10"	"16c"	"16"	"4"	0.03	"RE_12.3.3/12.9-10.7/12.9-10.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
65	"Qld_RE_DomE_12.3.3_16494"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	8.56989578775e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
66	"Qld_RE_DomE_12.3.3_16506"	"12.3.3/12.3.3a/12.3.3d"	"12.3.3"	"12.3.3a"	"12.3.3d"	" "	" "	"60/30/10"	60	30	10	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/18b/13d"	"60/30/10"	"16c"	"16"	"4"	8.79211349812e-03	"RE_12.3.3/12.3.3a/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
67	"Qld_RE_DomE_12.3.3_16512"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
68	"Qld_RE_DomE_12.3.3_16547"	"12.3.3/12.3.3a/12.3.3d"	"12.3.3"	"12.3.3a"	"12.3.3d"	" "	" "	"60/30/10"	60	30	10	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/18b/13d"	"60/30/10"	"16c"	"16"	"4"	0.02	"RE_12.3.3/12.3.3a/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
69	"Qld_RE_DomE_12.3.3_16556"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.53168063224e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
70	"Qld_RE_DomE_12.3.3_16586"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
71	"Qld_RE_DomE_12.3.3_16599"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	9.153921959e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
72	"Qld_RE_DomE_12.3.3_16606"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
73	"Qld_RE_DomE_12.3.3_16647"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	9.59984882298e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
74	"Qld_RE_DomE_12.3.3_16664"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
75	"Qld_RE_DomE_12.3.3_16705"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	7.48104265877e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
76	"Qld_RE_DomE_12.3.3_16733"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	7.56238450889e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
77	"Qld_RE_DomE_12.3.3_16743"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	7.31059807357e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
78	"Qld_RE_DomE_12.3.3_16753"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
79	"Qld_RE_DomE_12.3.3_16763"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.04308438205e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
80	"Qld_RE_DomE_12.3.3_16778"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
81	"Qld_RE_DomE_12.3.3_16783"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	2.79701983107e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
82	"Qld_RE_DomE_12.3.3_16806"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	9.10146121691e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
83	"Qld_RE_DomE_12.3.3_16828"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.04	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
84	"Qld_RE_DomE_12.3.3_16844"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
85	"Qld_RE_DomE_12.3.3_16864"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	8.74138053552e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
86	"Qld_RE_DomE_12.3.3_16886"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
87	"Qld_RE_DomE_12.3.3_16909"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
88	"Qld_RE_DomE_12.3.3_16923"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.47744960938e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
89	"Qld_RE_DomE_12.3.3_16925"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
90	"Qld_RE_DomE_12.3.3_16943"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	9.72597516913e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
91	"Qld_RE_DomE_12.3.3_16981"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	8.34541517147e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
92	"Qld_RE_DomE_12.3.3_17036"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	8.04018397038e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
93	"Qld_RE_DomE_12.3.3_17096"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.64561377347e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
94	"Qld_RE_DomE_12.3.3_17099"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
95	"Qld_RE_DomE_12.3.3_17120"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
96	"Qld_RE_DomE_12.3.3_17121"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	1.95983623559e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
97	"Qld_RE_DomE_12.3.3_17162"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.38193554581e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
98	"Qld_RE_DomE_12.3.3_17199"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
99	"Qld_RE_DomE_12.3.3_17202"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
100	"Qld_RE_DomE_12.3.3_17210"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	7.83195180797e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
101	"Qld_RE_DomE_12.3.3_17254"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
102	"Qld_RE_DomE_12.3.3_17290"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	9.39774067405e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
103	"Qld_RE_DomE_12.3.3_17326"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	5.63780847294e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
104	"Qld_RE_DomE_12.3.3_17328"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
105	"Qld_RE_DomE_12.3.3_17353"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.24059650486e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
106	"Qld_RE_DomE_12.3.3_17361"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.52844077278e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
107	"Qld_RE_DomE_12.3.3_17372"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
108	"Qld_RE_DomE_12.3.3_17377"	"12.3.3/12.3.8"	"12.3.3"	"12.3.8"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3/12.3.8"	"90/10"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c/34c"	"90/10"	"16c"	"16"	"4"	0.02	"RE_12.3.3/12.3.8"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
109	"Qld_RE_DomE_12.3.3_17388"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.91236151554e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
110	"Qld_RE_DomE_12.3.3_17392"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	5.48071974351e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
111	"Qld_RE_DomE_12.3.3_17427"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	9.29547043313e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
112	"Qld_RE_DomE_12.3.3_17438"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.98137711091e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
113	"Qld_RE_DomE_12.3.3_17490"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
114	"Qld_RE_DomE_12.3.3_17507"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	5.23657081066e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
115	"Qld_RE_DomE_12.3.3_17530"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	5.13698990269e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
116	"Qld_RE_DomE_12.3.3_17558"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	6.41754813222e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
117	"Qld_RE_DomE_12.3.3_17573"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	2.36584182263e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
212	"Qld_RE_DomE_12.3.3_18086"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
213	"Qld_RE_DomE_12.3.3_18087"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.95933613813e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
214	"Qld_RE_DomE_12.3.3_18088"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.28496503146e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
215	"Qld_RE_DomE_12.3.3_18116"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.02023364175e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
216	"Qld_RE_DomE_12.3.3_18124"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.78550061612e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
762	"Qld_RE_DomE_12.9-10.11_17259"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.64028637022e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
763	"Qld_RE_DomE_12.9-10.11_17263"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
764	"Qld_RE_DomE_12.9-10.11_17264"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.82696034016e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
765	"Qld_RE_DomE_12.9-10.11_17284"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.5763496622e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
771	"Qld_RE_DomE_12.9-10.11_17382"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
951	"Qld_RE_DomE_12.9-10.12_16976"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.05	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
952	"Qld_RE_DomE_12.9-10.12_16979"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.16	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
953	"Qld_RE_DomE_12.9-10.12_16985"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
954	"Qld_RE_DomE_12.9-10.12_16986"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.94672629298e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
955	"Qld_RE_DomE_12.9-10.12_16997"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.5562509689e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1242	"Qld_RE_DomE_12.9-10.16_19514"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.08	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1243	"Qld_RE_DomE_12.9-10.16_19525"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1244	"Qld_RE_DomE_12.9-10.16_19529"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.22	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1245	"Qld_RE_DomE_12.9-10.16_19530"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.05	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1246	"Qld_RE_DomE_12.9-10.16_19533"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
122	"Qld_RE_DomE_12.3.3_17608"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	2.0604701388e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
123	"Qld_RE_DomE_12.3.3_17612"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	3.38134184081e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
124	"Qld_RE_DomE_12.3.3_17622"	"12.3.3/12.3.3d"	"12.3.3"	"12.3.3d"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13d"	"90/10"	"16c"	"16"	"4"	5.18069147959e-03	"RE_12.3.3/12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
125	"Qld_RE_DomE_12.3.3_17640"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	8.17544160517e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
126	"Qld_RE_DomE_12.3.3_17642"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
127	"Qld_RE_DomE_12.3.3_17659"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
128	"Qld_RE_DomE_12.3.3_17669"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.93831635713e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
129	"Qld_RE_DomE_12.3.3_17675"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
130	"Qld_RE_DomE_12.3.3_17678"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
131	"Qld_RE_DomE_12.3.3_17696"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.89249164424e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
137	"Qld_RE_DomE_12.3.3_17741"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
138	"Qld_RE_DomE_12.3.3_17742"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
139	"Qld_RE_DomE_12.3.3_17746"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
140	"Qld_RE_DomE_12.3.3_17749"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
141	"Qld_RE_DomE_12.3.3_17752"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.59169766543e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
147	"Qld_RE_DomE_12.3.3_17800"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.12	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
148	"Qld_RE_DomE_12.3.3_17807"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.51938878505e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
149	"Qld_RE_DomE_12.3.3_17810"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
150	"Qld_RE_DomE_12.3.3_17813"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
151	"Qld_RE_DomE_12.3.3_17822"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.29902176703e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
152	"Qld_RE_DomE_12.3.3_17823"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.51721350922e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
153	"Qld_RE_DomE_12.3.3b_16881"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.08034958335e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
154	"Qld_RE_DomE_12.3.3b_16890"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
155	"Qld_RE_DomE_12.3.3b_16973"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
156	"Qld_RE_DomE_12.3.3b_16975"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
157	"Qld_RE_DomE_12.3.3b_16977"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.1761550432e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
158	"Qld_RE_DomE_12.9-10.11_17851"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	9.3603976559e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
159	"Qld_RE_DomE_12.9-10.11_17855"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.09230772431e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
160	"Qld_RE_DomE_12.9-10.11_17875"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
161	"Qld_RE_DomE_12.9-10.11_17886"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
162	"Qld_RE_DomE_12.9-10.11_17887"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.39323348567e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
163	"Qld_RE_DomE_12.9-10.12_16785"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	5.41545843114e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
164	"Qld_RE_DomE_12.9-10.12_16802"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
165	"Qld_RE_DomE_12.9-10.12_16825"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.09739270156e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
166	"Qld_RE_DomE_12.9-10.12_16829"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"85/15"	85	15	0	0	0	"12.9-10.12/12.9-10.19"	"85/15"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"85/15"	"9a"	"9"	"3"	0.12	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
167	"Qld_RE_DomE_12.9-10.12_16831"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.16	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
168	"Qld_RE_DomE_12.9-10.12_17196"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
169	"Qld_RE_DomE_12.9-10.12_17200"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
170	"Qld_RE_DomE_12.9-10.12_17206"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.42851701628e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
171	"Qld_RE_DomE_12.9-10.12_17209"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.06755072307e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
172	"Qld_RE_DomE_12.9-10.12_17217"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.26418548084e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
173	"Qld_RE_DomE_12.9-10.16_17739"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	6.39152567449e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
174	"Qld_RE_DomE_12.9-10.16_17766"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
175	"Qld_RE_DomE_12.9-10.16_17771"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	6.07140849569e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
176	"Qld_RE_DomE_12.9-10.16_17772"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
177	"Qld_RE_DomE_12.9-10.16_17781"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	5.9830013915e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
178	"Qld_RE_DomE_12.9-10.16_19459"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	6.40695197029e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
179	"Qld_RE_DomE_12.9-10.16_19463"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.05	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
180	"Qld_RE_DomE_12.9-10.16_19464"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	6.52522349455e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
181	"Qld_RE_DomE_12.9-10.16_19466"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	9.63155940721e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
182	"Qld_RE_DomE_12.9-10.16_19472"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	4.70571533036e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
183	"Qld_RE_DomE_12.9-10.6_18159"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	6.70525127068e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
184	"Qld_RE_DomE_12.9-10.6_18161"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	6.12954657198e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
185	"Qld_RE_DomE_12.9-10.6_18165"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.3466275649e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
186	"Qld_RE_DomE_12.9-10.6_18167"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.12903063783e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
187	"Qld_RE_DomE_12.9-10.6_18171"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	0.03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
188	"Qld_RE_DomE_12.3.3_17828"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	2.86087967037e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
189	"Qld_RE_DomE_12.3.3_17830"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.25093760778e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
190	"Qld_RE_DomE_12.3.3_17834"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.4555862732e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
191	"Qld_RE_DomE_12.3.3_17840"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.20669388396e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
192	"Qld_RE_DomE_12.3.3_17844"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	1.71346504389e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
193	"Qld_RE_DomE_12.3.3_17863"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.74539521019e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
194	"Qld_RE_DomE_12.3.3_17868"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.47392082393e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
195	"Qld_RE_DomE_12.3.3_17876"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.11995151291e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
196	"Qld_RE_DomE_12.3.3_17879"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.44547035741e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
197	"Qld_RE_DomE_12.3.3_17897"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
198	"Qld_RE_DomE_12.3.3_17902"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
199	"Qld_RE_DomE_12.3.3_17926"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	2.81278217062e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
200	"Qld_RE_DomE_12.3.3_17947"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.34191430578e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
201	"Qld_RE_DomE_12.3.3_17960"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.89126703344e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
202	"Qld_RE_DomE_12.3.3_17962"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	2.8963458899e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
203	"Qld_RE_DomE_12.3.3_18010"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	3.91448721033e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
204	"Qld_RE_DomE_12.3.3_18021"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
205	"Qld_RE_DomE_12.3.3_18058"	"12.3.3/12.3.7"	"12.3.3"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/16a"	"90/10"	"16c"	"16"	"4"	3.44918709607e-03	"RE_12.3.3/12.3.7"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
206	"Qld_RE_DomE_12.3.3_18059"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.02611070288e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
207	"Qld_RE_DomE_12.3.3_18071"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
208	"Qld_RE_DomE_12.3.3_18079"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	8.44602469398e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
209	"Qld_RE_DomE_12.3.3_18080"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.93367137084e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
210	"Qld_RE_DomE_12.3.3_18084"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.62014680814e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
211	"Qld_RE_DomE_12.3.3_18085"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"16c"	"100"	"16c"	"16"	"4"	3.43684143854e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
217	"Qld_RE_DomE_12.3.3_18127"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"16c"	"100"	"16c"	"16"	"4"	7.13230015819e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
218	"Qld_RE_DomE_12.3.3_18129"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	8.89649248798e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
219	"Qld_RE_DomE_12.3.3_18134"	"12.3.3/12.3.7"	"12.3.3"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/16a"	"90/10"	"16c"	"16"	"4"	0.01	"RE_12.3.3/12.3.7"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
220	"Qld_RE_DomE_12.3.3_18135"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.58409078543e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
221	"Qld_RE_DomE_12.3.3_18158"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
222	"Qld_RE_DomE_12.3.3_18179"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
223	"Qld_RE_DomE_12.3.3_18184"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
224	"Qld_RE_DomE_12.3.3_18191"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	3.86466390614e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
225	"Qld_RE_DomE_12.3.3_18205"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"16c"	"100"	"16c"	"16"	"4"	8.57758177108e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
226	"Qld_RE_DomE_12.3.3_18208"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	3.8835371687e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
227	"Qld_RE_DomE_12.3.3_18262"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.55869854252e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
228	"Qld_RE_DomE_12.3.3_18297"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	2.54568272241e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
229	"Qld_RE_DomE_12.3.3_18300"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.92253871472e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
230	"Qld_RE_DomE_12.3.3_18315"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.92433345964e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
231	"Qld_RE_DomE_12.3.3_18316"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	5.40792403467e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
232	"Qld_RE_DomE_12.3.3_18326"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.92764217792e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
233	"Qld_RE_DomE_12.3.3_18340"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	7.82694776495e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
234	"Qld_RE_DomE_12.3.3_18342"	"12.3.3/12.3.8"	"12.3.3"	"12.3.8"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.3.3/12.3.8"	"60/40"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c/34c"	"60/40"	"16c"	"16"	"4"	0.02	"RE_12.3.3/12.3.8"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
235	"Qld_RE_DomE_12.3.3_18366"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	7.44053267798e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
236	"Qld_RE_DomE_12.3.3_18371"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	8.69786589336e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
237	"Qld_RE_DomE_12.3.3_18375"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	4.72846445317e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
238	"Qld_RE_DomE_12.3.3_18376"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	5.03921122484e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
239	"Qld_RE_DomE_12.3.3_18378"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	9.94872786313e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
240	"Qld_RE_DomE_12.3.3_18379"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.01563468506e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
241	"Qld_RE_DomE_12.3.3_18380"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.21947213597e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
247	"Qld_RE_DomE_12.3.3_18442"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	3.66443907871e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
248	"Qld_RE_DomE_12.3.3_18462"	"12.3.3/12.3.7"	"12.3.3"	"12.3.7"	" "	" "	" "	"85/15"	85	15	0	0	0	"12.3.3/12.3.7"	"85/15"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c/16a"	"85/15"	"16c"	"16"	"4"	5.64601665184e-03	"RE_12.3.3/12.3.7"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
249	"Qld_RE_DomE_12.3.3_18489"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
250	"Qld_RE_DomE_12.3.3_18494"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.92808782367e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
251	"Qld_RE_DomE_12.3.3_18538"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
252	"Qld_RE_DomE_12.3.3_18539"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	7.02263502656e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
253	"Qld_RE_DomE_12.3.3_18569"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.64893708153e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
254	"Qld_RE_DomE_12.3.3_18587"	"12.3.3/12.9-10.7/12.9-10.3"	"12.3.3"	"12.9-10.7"	"12.9-10.3"	" "	" "	"60/30/10"	60	30	10	0	0	"12.3.3/12.9-10.7/12.9-10.3"	"60/30/10"	"3"	"E/OC/OC"	254	"E/O/O"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c/13c/13d"	"60/30/10"	"16c"	"16"	"4"	0.01	"RE_12.3.3/12.9-10.7/12.9-10.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
255	"Qld_RE_DomE_12.3.3_18593"	"12.3.3/12.9-10.7"	"12.3.3"	"12.9-10.7"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.3.3/12.9-10.7"	"60/40"	"3"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c/13c"	"60/40"	"16c"	"16"	"4"	3.19772733493e-03	"RE_12.3.3/12.9-10.7"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
256	"Qld_RE_DomE_12.3.3_18604"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	9.85946572169e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
257	"Qld_RE_DomE_12.3.3_18611"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
258	"Qld_RE_DomE_12.3.3_18710"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
259	"Qld_RE_DomE_12.3.3_18747"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.84723969387e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
260	"Qld_RE_DomE_12.3.3_18755"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	8.83443176987e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
261	"Qld_RE_DomE_12.3.3_18760"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.95513611004e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
262	"Qld_RE_DomE_12.3.3_18761"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.49589175193e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
263	"Qld_RE_DomE_12.3.3_18766"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	4.09739033854e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
264	"Qld_RE_DomE_12.3.3_18786"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	9.37462044966e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
265	"Qld_RE_DomE_12.3.3_18812"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	2.89193999968e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
266	"Qld_RE_DomE_12.3.3_18818"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.28186602476e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
267	"Qld_RE_DomE_12.3.3_18836"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	7.59844513593e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
268	"Qld_RE_DomE_12.3.3_18865"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	100	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	3.81470232646e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
269	"Qld_RE_DomE_12.3.3_18867"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.96874322805e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
270	"Qld_RE_DomE_12.3.3_18898"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
281	"Qld_RE_DomE_12.3.3_19145"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	6.03275515833e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
282	"Qld_RE_DomE_12.3.3_19158"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
283	"Qld_RE_DomE_12.3.3_19186"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	5.1936590209e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
284	"Qld_RE_DomE_12.3.3_19194"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	9.14563789542e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
285	"Qld_RE_DomE_12.3.3_19202"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
907	"Qld_RE_DomE_12.9-10.12_16531"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
908	"Qld_RE_DomE_12.9-10.12_16550"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
909	"Qld_RE_DomE_12.9-10.12_16553"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	3.41149519957e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
910	"Qld_RE_DomE_12.9-10.12_16557"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
911	"Qld_RE_DomE_12.9-10.12_16563"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	6.38363199696e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
974	"Qld_RE_DomE_12.9-10.12_17131"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.15611034772e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
975	"Qld_RE_DomE_12.9-10.12_17138"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.65824064784e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
976	"Qld_RE_DomE_12.9-10.12_17140"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.96876949096e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
977	"Qld_RE_DomE_12.9-10.12_17142"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
978	"Qld_RE_DomE_12.9-10.12_17144"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
286	"Qld_RE_DomE_12.3.3_19204"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.02	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
287	"Qld_RE_DomE_12.3.3_19222"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.63301551001e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
288	"Qld_RE_DomE_12.3.3_19226"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	6.80797357193e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
289	"Qld_RE_DomE_12.3.3_19230"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
290	"Qld_RE_DomE_12.3.3_19231"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	7.10779614361e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
291	"Qld_RE_DomE_12.3.3_19245"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
292	"Qld_RE_DomE_12.3.3_19247"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
293	"Qld_RE_DomE_12.3.3_19265"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
294	"Qld_RE_DomE_12.3.3_19266"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
295	"Qld_RE_DomE_12.3.3_19276"	"12.3.3/12.3.7"	"12.3.3"	"12.3.7"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.3.3/12.3.7"	"70/30"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c/16a"	"70/30"	"16c"	"16"	"4"	0.01	"RE_12.3.3/12.3.7"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
296	"Qld_RE_DomE_12.3.3_19298"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"16c"	"100"	"16c"	"16"	"4"	8.52017254273e-03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
297	"Qld_RE_DomE_12.3.3_19300"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
298	"Qld_RE_DomE_12.3.3_19325"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"16c"	"100"	"16c"	"16"	"4"	0.01	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
299	"Qld_RE_DomE_12.3.3_19370"	"12.3.3/12.3.7"	"12.3.3"	"12.3.7"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.3.3/12.3.7"	"90/10"	"3"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c/16a"	"90/10"	"16c"	"16"	"4"	0.04	"RE_12.3.3/12.3.7"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
300	"Qld_RE_DomE_12.3.3_19557"	"12.3.3"	"12.3.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"16c"	"100"	"16c"	"16"	"4"	0.03	"RE_12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
301	"Qld_RE_DomE_12.3.3a_16839"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	0.01	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
302	"Qld_RE_DomE_12.3.3a_16840"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	0.01	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
303	"Qld_RE_DomE_12.3.3a_16856"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	6.70113315381e-03	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
304	"Qld_RE_DomE_12.3.3a_16866"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	0.01	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
305	"Qld_RE_DomE_12.3.3a_16873"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	0.01	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
306	"Qld_RE_DomE_12.3.3a_16951"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	3.10966819939e-03	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
307	"Qld_RE_DomE_12.3.3a_17149"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	0.01	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
308	"Qld_RE_DomE_12.3.3a_17180"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	2.45996663474e-03	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
309	"Qld_RE_DomE_12.3.3a_17349"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	3.61728267673e-03	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
310	"Qld_RE_DomE_12.3.3a_17371"	"12.3.3a"	"12.3.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"18b"	"100"	"18b"	"18"	"5"	0.03	"RE_12.3.3a"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
311	"Qld_RE_DomE_12.3.3b_16508"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	6.92179915073e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
312	"Qld_RE_DomE_12.3.3b_16525"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.34410016059e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
313	"Qld_RE_DomE_12.3.3b_16536"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
314	"Qld_RE_DomE_12.3.3b_16539"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.87511205549e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
315	"Qld_RE_DomE_12.3.3b_16554"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.97774148788e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
316	"Qld_RE_DomE_12.3.3b_16699"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
317	"Qld_RE_DomE_12.3.3b_16784"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
318	"Qld_RE_DomE_12.3.3b_16801"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
319	"Qld_RE_DomE_12.3.3b_16820"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	7.25581349598e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
320	"Qld_RE_DomE_12.3.3b_16821"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
326	"Qld_RE_DomE_12.3.3b_16880"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
327	"Qld_RE_DomE_12.3.3b_16991"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.81537812258e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
328	"Qld_RE_DomE_12.3.3b_17000"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.56550565823e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
329	"Qld_RE_DomE_12.3.3b_17005"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	8.36796554108e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
330	"Qld_RE_DomE_12.3.3b_17012"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.34351531926e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
336	"Qld_RE_DomE_12.3.3b_17102"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	5.25277182738e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
337	"Qld_RE_DomE_12.3.3b_17272"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
338	"Qld_RE_DomE_12.3.3b_17416"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.5840427037e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
339	"Qld_RE_DomE_12.3.3b_17426"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
340	"Qld_RE_DomE_12.3.3b_17546"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
341	"Qld_RE_DomE_12.3.3b_17552"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	6.11960351587e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
342	"Qld_RE_DomE_12.3.3b_17587"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	6.86808539843e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
343	"Qld_RE_DomE_12.3.3b_17591"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.17106282702e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
344	"Qld_RE_DomE_12.3.3b_17610"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.82332563865e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
345	"Qld_RE_DomE_12.3.3b_17620"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	8.5711240399e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
346	"Qld_RE_DomE_12.3.3b_17651"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
347	"Qld_RE_DomE_12.3.3b_17816"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	8.1085402878e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
348	"Qld_RE_DomE_12.3.3b_17839"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	7.92638916812e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
349	"Qld_RE_DomE_12.3.3b_17850"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	8.91853765212e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
350	"Qld_RE_DomE_12.3.3b_17864"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	2.56531476467e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
351	"Qld_RE_DomE_12.3.3b_17872"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
352	"Qld_RE_DomE_12.3.3b_17882"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	4.77392504633e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
353	"Qld_RE_DomE_12.3.3b_17904"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	2.43659804883e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
354	"Qld_RE_DomE_12.3.3b_17907"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.74996885704e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
355	"Qld_RE_DomE_12.3.3b_17911"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	5.06477889161e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
356	"Qld_RE_DomE_12.3.3b_17916"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	4.80587195769e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
357	"Qld_RE_DomE_12.3.3b_17919"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	4.41143732687e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
358	"Qld_RE_DomE_12.3.3b_17928"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	8.03522915069e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
359	"Qld_RE_DomE_12.3.3b_17933"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.22817984703e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
360	"Qld_RE_DomE_12.3.3b_17945"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	1.84273964621e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
361	"Qld_RE_DomE_12.3.3b_17951"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	2.40253835895e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
362	"Qld_RE_DomE_12.3.3b_17955"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.98204730525e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
363	"Qld_RE_DomE_12.3.3b_17956"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	3.2964711632e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
364	"Qld_RE_DomE_12.3.3b_17958"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	8.88110469939e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
365	"Qld_RE_DomE_12.3.3b_17963"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.36404646201e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
366	"Qld_RE_DomE_12.3.3b_17964"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
367	"Qld_RE_DomE_12.3.3b_17966"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	5.63307683333e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
368	"Qld_RE_DomE_12.3.3b_17972"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
369	"Qld_RE_DomE_12.3.3b_17980"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
370	"Qld_RE_DomE_12.3.3b_17982"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	7.39271970376e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
371	"Qld_RE_DomE_12.3.3b_17987"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	6.92565677547e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
372	"Qld_RE_DomE_12.3.3b_17988"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
373	"Qld_RE_DomE_12.3.3b_17995"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
374	"Qld_RE_DomE_12.3.3b_17997"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	5.52155734079e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
375	"Qld_RE_DomE_12.3.3b_18011"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	2.94749290254e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
376	"Qld_RE_DomE_12.3.3b_18028"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	4.12860358074e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
377	"Qld_RE_DomE_12.3.3b_18032"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	6.87659322254e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
378	"Qld_RE_DomE_12.3.3b_18034"	"12.3.3b"	"12.3.3b"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	4.44259306136e-03	"RE_12.3.3b"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
379	"Qld_RE_DomE_12.3.3c_16515"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.13193777175e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
380	"Qld_RE_DomE_12.3.3c_16568"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.71416068621e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
381	"Qld_RE_DomE_12.3.3c_16759"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.52334228458e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
382	"Qld_RE_DomE_12.3.3c_16786"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
383	"Qld_RE_DomE_12.3.3c_16791"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	9.56256228282e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
384	"Qld_RE_DomE_12.3.3c_16794"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.22057889804e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
385	"Qld_RE_DomE_12.3.3c_16796"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.07965347661e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
386	"Qld_RE_DomE_12.3.3c_16812"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.96571771093e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
387	"Qld_RE_DomE_12.3.3c_16822"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.27077564798e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
388	"Qld_RE_DomE_12.3.3c_16838"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.3212625272e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
389	"Qld_RE_DomE_12.3.3c_16876"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.36669069528e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
390	"Qld_RE_DomE_12.3.3c_16882"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.83585702329e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
391	"Qld_RE_DomE_12.3.3c_16885"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
392	"Qld_RE_DomE_12.3.3c_16894"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.50138987105e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
393	"Qld_RE_DomE_12.3.3c_16901"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.85115033349e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
394	"Qld_RE_DomE_12.3.3c_16940"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	8.17688790209e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
395	"Qld_RE_DomE_12.3.3c_16956"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.46996842457e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
396	"Qld_RE_DomE_12.3.3c_16961"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.59733153593e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
397	"Qld_RE_DomE_12.3.3c_16989"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.96517283455e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
398	"Qld_RE_DomE_12.3.3c_16993"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.87766090056e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
399	"Qld_RE_DomE_12.3.3c_17001"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.69747491341e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
400	"Qld_RE_DomE_12.3.3c_17006"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.18988085096e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
406	"Qld_RE_DomE_12.3.3c_17062"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.48392105661e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
407	"Qld_RE_DomE_12.3.3c_17109"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
408	"Qld_RE_DomE_12.3.3c_17172"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.65381366317e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
409	"Qld_RE_DomE_12.3.3c_17178"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.66159578307e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
410	"Qld_RE_DomE_12.3.3c_17250"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.80640320033e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
411	"Qld_RE_DomE_12.3.3c_17277"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.69449584291e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
412	"Qld_RE_DomE_12.3.3c_17296"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.80518541798e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
413	"Qld_RE_DomE_12.3.3c_17419"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.42282631718e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
414	"Qld_RE_DomE_12.3.3c_17561"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	8.72047600584e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
415	"Qld_RE_DomE_12.3.3c_17570"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.54206885426e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
416	"Qld_RE_DomE_12.3.3c_17579"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.02399222791e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
417	"Qld_RE_DomE_12.3.3c_17625"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.7380704917e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
418	"Qld_RE_DomE_12.3.3c_17837"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.40442396674e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
419	"Qld_RE_DomE_12.3.3c_17849"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.27596770503e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
420	"Qld_RE_DomE_12.3.3c_17881"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.55307365851e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
431	"Qld_RE_DomE_12.3.3d_16695"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	4.73874048658e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
432	"Qld_RE_DomE_12.3.3d_16713"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	2.60206470995e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
433	"Qld_RE_DomE_12.3.3d_16720"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	2.367815397e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
434	"Qld_RE_DomE_12.3.3d_16734"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	9.58410050854e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
435	"Qld_RE_DomE_12.3.3d_16765"	"12.3.3d/12.3.3"	"12.3.3d"	"12.3.3"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d/16c"	"70/30"	"13d"	"13"	"3"	9.58838273667e-03	"RE_12.3.3d/12.3.3"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
671	"Qld_RE_DomE_12.8.24_18571"	"12.8.24/12.8.9"	"12.8.24"	"12.8.9"	" "	" "	" "	"65/35"	65	35	0	0	0	"12.8.24/12.8.9"	"65/35"	"8"	"E/OC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b/8a"	"65/35"	"10b"	"10"	"3"	0.03	"RE_12.8.24/12.8.9"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
672	"Qld_RE_DomE_12.8.24_18576"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	5.14415155887e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
673	"Qld_RE_DomE_12.8.24_18579"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	9.06210995652e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
674	"Qld_RE_DomE_12.8.24_18586"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
675	"Qld_RE_DomE_12.8.24_18591"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
807	"Qld_RE_DomE_12.9-10.11a_17087"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
808	"Qld_RE_DomE_12.9-10.11a_17088"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.33657994953e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
809	"Qld_RE_DomE_12.9-10.11a_17090"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
810	"Qld_RE_DomE_12.9-10.11a_17093"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.02	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
811	"Qld_RE_DomE_12.9-10.11a_17095"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	9.7631408829e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
897	"Qld_RE_DomE_12.9-10.12_16476"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	5.541634621e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
898	"Qld_RE_DomE_12.9-10.12_16485"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	4.98788944425e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
899	"Qld_RE_DomE_12.9-10.12_16498"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.29279714552e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
900	"Qld_RE_DomE_12.9-10.12_16500"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	2.71971590909e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
901	"Qld_RE_DomE_12.9-10.12_16504"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	1.98167917654e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1074	"Qld_RE_DomE_12.9-10.12_17609"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1075	"Qld_RE_DomE_12.9-10.12_17613"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.39001505959e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1076	"Qld_RE_DomE_12.9-10.12_17616"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.43291782234e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1077	"Qld_RE_DomE_12.9-10.12_17624"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1078	"Qld_RE_DomE_12.9-10.12_17628"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.13869600598e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
421	"Qld_RE_DomE_12.3.3c_17915"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
422	"Qld_RE_DomE_12.3.3c_17943"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.17507144364e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
423	"Qld_RE_DomE_12.3.3c_17959"	"12.3.3c"	"12.3.3c"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.11842254896e-03	"RE_12.3.3c"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
424	"Qld_RE_DomE_12.3.3d_16020"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
425	"Qld_RE_DomE_12.3.3d_16481"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
441	"Qld_RE_DomE_12.3.3d_16852"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	1.84101164834e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
442	"Qld_RE_DomE_12.3.3d_16884"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
443	"Qld_RE_DomE_12.3.3d_16924"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
444	"Qld_RE_DomE_12.3.3d_16934"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	3.67080370576e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
445	"Qld_RE_DomE_12.3.3d_16954"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
446	"Qld_RE_DomE_12.3.3d_17387"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
447	"Qld_RE_DomE_12.3.3d_17403"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	8.48990136679e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
448	"Qld_RE_DomE_12.3.3d_17406"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
449	"Qld_RE_DomE_12.3.3d_17408"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
450	"Qld_RE_DomE_12.3.3d_17410"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
451	"Qld_RE_DomE_12.3.3d_17422"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
452	"Qld_RE_DomE_12.3.3d_17443"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	2.72293744351e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
453	"Qld_RE_DomE_12.3.3d_17447"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	4.03697951516e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
454	"Qld_RE_DomE_12.3.3d_17451"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	4.74543287849e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
455	"Qld_RE_DomE_12.3.3d_17457"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
456	"Qld_RE_DomE_12.3.3d_17464"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	2.87164785393e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
457	"Qld_RE_DomE_12.3.3d_17470"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	8.24408721356e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
458	"Qld_RE_DomE_12.3.3d_17471"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	4.40744033578e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
459	"Qld_RE_DomE_12.3.3d_17505"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
460	"Qld_RE_DomE_12.3.3d_17602"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	6.90121053468e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
461	"Qld_RE_DomE_12.3.3d_17939"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"13d"	"100"	"13d"	"13"	"3"	6.00621593595e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
462	"Qld_RE_DomE_12.3.3d_18221"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	7.23245054332e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
463	"Qld_RE_DomE_12.3.3d_18233"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.01	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
464	"Qld_RE_DomE_12.3.3d_18246"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	0.02	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
465	"Qld_RE_DomE_12.3.3d_18274"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	7.93882151648e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
466	"Qld_RE_DomE_12.3.3d_18714"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	6.10011612629e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
467	"Qld_RE_DomE_12.3.3d_18803"	"12.3.3d"	"12.3.3d"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.3.3"	"100"	"3"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"13d"	"100"	"13d"	"13"	"3"	8.867944281e-03	"RE_12.3.3d"	"12.3.3"	120303.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus tereticornis woodland. Eucalyptus crebra and E. moluccana are sometimes present and may be relatively abundant in places, especially on edges of plains and higher level alluvium. Other species that may be present as scattered individuals or clumps include Angophora subvelutina or A. floribunda, Corymbia clarksoniana, C. intermedia, C. tessellaris, Lophostemon suaveolens and E. melanophloia. Occurs on Quaternary alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 16c)
 Vegetation communities in this regional ecosystem include: 
12.3.3a: Floodplain (other than floodplain wetlands). Eucalyptus crebra, C. tessellaris woodland to open forest. Other species that may be present as scattered individuals or clumps include Corymbia clarksoniana, Eucalyptus melanophloia, E. tereticornis and C. citriodora subsp. variegata. Occurs on high level alluvial plains, terraces and fans where rainfall is usually less than 1000mm/y. (BVG1M: 18b)
12.3.3b: Floodplain (other than floodplain wetlands). Open forest to woodland of Eucalyptus moluccana and/or Eucalyptus tereticornis and E. crebra, with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on margins of Quaternary alluvial plains. (BVG1M: 13d)
12.3.3c: Floodplain (other than floodplain wetlands). Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora may be present. Occurs on Quaternary alluvial plains where drainage of soils is impeded. (BVG1M: 21b)
12.3.3d: Floodplain (other than floodplain wetlands). Eucalyptus moluccana woodland. Other frequently occurring species include Eucalyptus tereticornis, E. crebra, E. siderophloia and Corymbia intermedia. Occurs on margins of Quaternary alluvial plains usually adjacent sedimentary geologies. (BVG1M: 13d)"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Eucalyptus tereticornis woodland on Quaternary alluvium"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), E10."	"2, 10, 5, 6, 7, 8, (3)"	"Bulburin NP, Eurimbula NP, Littabella NP, Curtis Island NP, Good Night Scrub NP, Bunya Mountains NP, Beninbi NP, Warro NP, Mount Colosseum NP, Bania NP, Curtis Island CP, Dawes NP, Nour Nour NP, Southend CP, Grongah NP, Bottle Creek CP, Mount Barney NP, Kroombit Tops NP, Burrum Coast NP, Woowoonga NP, Baywulla Creek CP, Main Range NP, Tarong NP, Baffle Creek CP, White Rock CP, Calliope CP, Lockyer NP (R), Mouth of Kolan River CP, Mount Walsh NP, Deepwater NP, Castle Tower NP, [Flagstone Creek CP], [Lockyer NP], [D'Aguilar NP], [Gatton NP], [Mouth of Baffle Creek CP 2], [Cherbourg NP], [Lockyer RR], [Dawes NP (R)]"	"Habitat for threatened flora species including Rhaponticum australe.
12.3.3a: Habitat for threatened flora species including occasional Rhaponticum australe.
12.3.3b: Habitat for threatened flora species including Melaleuca irbyana.
12.3.3c: Habitat for threatened flora species including Melaleuca irbyana and Marsdenia coronata.
12.3.3d: Habitat for threatened flora species including Rhaponticum australe."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.3.3: Sub-coastal and inland parts of bioregion. Also occurs in coastal areas north of Bundaberg. While Eucalyptus tereticornis remains common in the landscape, very few intact stands remain. Eucalyptus tereticornis grows into a very large hollow-forming tree and has a special significance for fauna species, especially in drier areas. The type is variable, ranging from woodland in drier parts to tall open forest in higher rainfall areas and mono-specific to mixed with other canopy species. Eucalyptus tereticornis will regenerate readily but there is a lack of recruitment to replace old trees in stands that are logged, thinned or grazed and regularly burnt. The grasses and herbs associated with intact Eucalyptus tereticornis communities also persist in the landscape, so there is a potential for re-establishing the RE and increasing its remnant area. Eucalyptus tereticornis is replaced by E. grandis in highest-rainfall parts of the bioregion.
12.3.3a: Sub-coastal and inland parts of bioregion. Characteristic localities include Burnett River catchment and Ripley Valley. Too small to map at 1:100 000 scale.
12.3.3b: Restricted to the Ipswich and Jimboomba regions.
12.3.3c: Restricted to the Ipswich and Jimboomba regions. This floristic association on land zone 9-10 is mapped as 12.9-10.11."		12.00	3.00	"Floodplain (other than floodplain wetlands)."	"Sparse"	"W"	"16c"
468	"Qld_RE_DomE_12.5.2a_15900"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
469	"Qld_RE_DomE_12.5.2a_15912"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.23674838896e-03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
470	"Qld_RE_DomE_12.5.2a_16009"	"12.5.2a/12.5.3a"	"12.5.2a"	"12.5.3a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.2/12.5.3"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.06161444362e-03	"RE_12.5.2a/12.5.3a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
471	"Qld_RE_DomE_12.5.2a_16030"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
472	"Qld_RE_DomE_12.5.2a_16046"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
473	"Qld_RE_DomE_12.5.2a_16053"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.51883342665e-03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
474	"Qld_RE_DomE_12.5.2a_16056"	"12.5.2a/12.5.3a"	"12.5.2a"	"12.5.3a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.2/12.5.3"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.87130053425e-03	"RE_12.5.2a/12.5.3a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
596	"Qld_RE_DomE_12.5.3a_16394"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.43089108209e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
532	"Qld_RE_DomE_12.5.3a_16118"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	2.93256828117e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
533	"Qld_RE_DomE_12.5.3a_16122"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	8.5842945874e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
534	"Qld_RE_DomE_12.5.3a_16124"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.33390526964e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
535	"Qld_RE_DomE_12.5.3a_16125"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.20928985575e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
536	"Qld_RE_DomE_12.5.3a_16136"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.46920253077e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
537	"Qld_RE_DomE_12.5.3a_16145"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.06702346389e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
1069	"Qld_RE_DomE_12.9-10.12_17600"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.53165851608e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1070	"Qld_RE_DomE_12.9-10.12_17603"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.21826727376e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1071	"Qld_RE_DomE_12.9-10.12_17604"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.05	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1072	"Qld_RE_DomE_12.9-10.12_17605"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.50504228975e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1073	"Qld_RE_DomE_12.9-10.12_17607"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.13286391077e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
676	"Qld_RE_DomE_12.8.24_18598"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.06	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
677	"Qld_RE_DomE_12.8.24_18606"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.07	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
678	"Qld_RE_DomE_12.8.24_18614"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	5.9358857555e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
679	"Qld_RE_DomE_12.8.24_18615"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	8.3271396362e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
680	"Qld_RE_DomE_12.8.24_18641"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.05	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
716	"Qld_RE_DomE_12.8.24_19374"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.07	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
717	"Qld_RE_DomE_12.8.24_19379"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.09	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
718	"Qld_RE_DomE_12.8.24_19398"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.05	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
719	"Qld_RE_DomE_12.8.24_19406"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
720	"Qld_RE_DomE_12.8.24_19409"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	5.79459080836e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
877	"Qld_RE_DomE_12.9-10.12_15908"	"12.9-10.12/12.9-10.17b"	"12.9-10.12"	"12.9-10.17b"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.17"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.17b"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
878	"Qld_RE_DomE_12.9-10.12_15935"	"12.9-10.12/12.9-10.17b"	"12.9-10.12"	"12.9-10.17b"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.17"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	8.72552303042e-03	"RE_12.9-10.12/12.9-10.17b"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
879	"Qld_RE_DomE_12.9-10.12_15949"	"12.9-10.12/12.9-10.17b"	"12.9-10.12"	"12.9-10.17b"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.17"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12/12.9-10.17b"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
880	"Qld_RE_DomE_12.9-10.12_15953"	"12.9-10.12/12.9-10.17b"	"12.9-10.12"	"12.9-10.17b"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.17"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.17b"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
937	"Qld_RE_DomE_12.9-10.12_16853"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.05	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
938	"Qld_RE_DomE_12.9-10.12_16863"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
939	"Qld_RE_DomE_12.9-10.12_16897"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"85/15"	85	15	0	0	0	"12.9-10.12/12.9-10.19"	"85/15"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"85/15"	"9a"	"9"	"3"	6.73596990881e-03	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
940	"Qld_RE_DomE_12.9-10.12_16903"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1227	"Qld_RE_DomE_12.9-10.16_19431"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1228	"Qld_RE_DomE_12.9-10.16_19438"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	5.91000711315e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1229	"Qld_RE_DomE_12.9-10.16_19451"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1230	"Qld_RE_DomE_12.9-10.16_19453"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	8.90582141989e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1231	"Qld_RE_DomE_12.9-10.16_19455"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
597	"Qld_RE_DomE_12.5.3a_16412"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.96257338372e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
598	"Qld_RE_DomE_12.5.3a_16416"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.33932281585e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
599	"Qld_RE_DomE_12.5.3a_16420"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.07755126518e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
600	"Qld_RE_DomE_12.5.3a_16423"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
601	"Qld_RE_DomE_12.5.3a_16424"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.92143153386e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
777	"Qld_RE_DomE_12.9-10.11_17646"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.30343648002e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
778	"Qld_RE_DomE_12.9-10.11_17759"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.05380058513e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
779	"Qld_RE_DomE_12.9-10.11_17821"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.55479095111e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
780	"Qld_RE_DomE_12.9-10.11_17842"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.47958840405e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
781	"Qld_RE_DomE_12.9-10.11_17847"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.31079691972e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
980	"Qld_RE_DomE_12.9-10.12_17147"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.19"	"60/40"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"60/40"	"9a"	"9"	"3"	9.21638260615e-03	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
981	"Qld_RE_DomE_12.9-10.12_17151"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
982	"Qld_RE_DomE_12.9-10.12_17157"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.56744544374e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
983	"Qld_RE_DomE_12.9-10.12_17158"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
984	"Qld_RE_DomE_12.9-10.12_17164"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.25800185079e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1195	"Qld_RE_DomE_12.9-10.16_18857"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1196	"Qld_RE_DomE_12.9-10.16_19065"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1197	"Qld_RE_DomE_12.9-10.16_19147"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	6.76165305591e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1198	"Qld_RE_DomE_12.9-10.16_19154"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	4.85185562369e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1199	"Qld_RE_DomE_12.9-10.16_19157"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1287	"Qld_RE_DomE_12.9-10.6_18296"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	6.78699224371e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1288	"Qld_RE_DomE_12.9-10.6_18336"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.406536577e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1289	"Qld_RE_DomE_12.9-10.6_18352"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	0.01	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1290	"Qld_RE_DomE_12.9-10.6_18355"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	9.47984555416e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1291	"Qld_RE_DomE_12.9-10.6_18356"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	9.0159235451e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
475	"Qld_RE_DomE_12.5.2a_16083"	"12.5.2a/12.5.3a"	"12.5.2a"	"12.5.3a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.2/12.5.3"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.13104278722e-03	"RE_12.5.2a/12.5.3a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
476	"Qld_RE_DomE_12.5.2a_16089"	"12.5.2a/12.5.3a"	"12.5.2a"	"12.5.3a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.2/12.5.3"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.02	"RE_12.5.2a/12.5.3a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
477	"Qld_RE_DomE_12.5.2a_16096"	"12.5.2a/12.5.3a"	"12.5.2a"	"12.5.3a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.2/12.5.3"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.02	"RE_12.5.2a/12.5.3a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
478	"Qld_RE_DomE_12.5.2a_16140"	"12.5.2a/12.5.3a"	"12.5.2a"	"12.5.3a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.2/12.5.3"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	1.85452633179e-03	"RE_12.5.2a/12.5.3a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
479	"Qld_RE_DomE_12.5.2a_16143"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.68485046206e-03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
480	"Qld_RE_DomE_12.5.2a_16151"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.42523221078e-03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
481	"Qld_RE_DomE_12.5.2a_16207"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.54597323232e-03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
482	"Qld_RE_DomE_12.5.2a_16242"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	9.3776238907e-03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
483	"Qld_RE_DomE_12.5.2a_16285"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
484	"Qld_RE_DomE_12.5.2a_16324"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
485	"Qld_RE_DomE_12.5.2a_16338"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	9.25356170793e-03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
486	"Qld_RE_DomE_12.5.2a_16388"	"12.5.2a"	"12.5.2a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.2"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9g"	"100"	"9g"	"9"	"3"	8.92372988329e-03	"RE_12.5.2a"	"12.5.2"	120502.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Corymbia intermedia, Eucalyptus tereticornis grassy open forest to woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. Usually deep red soils. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.2a:  Corymbia intermedia, Eucalyptus tereticornis woodland. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides or E. portuensis, E. siderophloia or E. crebra, Corymbia tessellaris and Melaleuca quinquenervia (lower slopes). Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments usually in coastal areas with deep red soils. (BVG1M: 9g)
12.5.2b:  Eucalyptus tereticornis +/- Corymbia intermedia open forest. Other species can include Lophostemon suaveolens, Angophora leiocarpa, Eucalyptus acmenoides, E. crebra, Corymbia tessellaris and C. citriodora subsp. Variegata. Eucalyptus exserta is usually present in northern parts of bioregion. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments in sub-coastal areas. Usually deep red soils. (BVG1M: 9g)
12.5.2x1:  Melaleuca irbyana low open forest with emergent Eucalyptus tereticornis. Occurs on remnant Tertiary surfaces, mainly deeply weathered high level Tertiary alluvium. (BVG1M: 21b)"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Corymbia intermedia, Eucalyptus tereticornis open forest on remnant Tertiary surfaces, usually near coast. Usually deep red soils"	"Bean et al. (1998), G39"	"8, 4, 2, 10, 6, 5, 7, (9), (3)"	"Great Sandy NP, Teerk Roo Ra NP (IJMA), Mount Binga NP, Teerk Roo Ra CP (IJMA), Deepwater NP, Tewantin NP, Tingalpa Creek CP, Littabella NP"	"Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Summer to late-autumn. INTENSITY: Low. INTERVAL: 3-6 years. STRATEGY: Aim to burn 40-60% of any given area. Spot ignition in cooler or moister periods encourages mosaics. ISSUES: Control of weeds is a major focus of planned burning in most areas. Maintain ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas."	"12.5.2: Coastal and sub coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2a: Coastal areas. Has been extensively cleared for horticulture, sugar cane and urban development. Areas of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are mapped as the lower slope component of 12.9-10.4.
12.5.2b: Sub-coastal areas. Has been extensively cleared for horticulture and grazing.
12.5.2x1: Restricted to one location south of Toogoolawah Mostly cleared for pasture. This floristic association on land zone 9-10 is mapped as 12.9-10.11 and on land zone 3 is mapped as 12.3.3c."		12.00	5.00		"Mid-dense"	"OF"	"9g"
487	"Qld_RE_DomE_12.5.3_15736"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
488	"Qld_RE_DomE_12.5.3_15769"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"C"	"9g"	"100"	"9g"	"9"	"3"	6.19131447761e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
489	"Qld_RE_DomE_12.5.3_15834"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
490	"Qld_RE_DomE_12.5.3_15848"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.72989613091e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
491	"Qld_RE_DomE_12.5.3_15871"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
492	"Qld_RE_DomE_12.5.3_15880"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.38398089213e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
493	"Qld_RE_DomE_12.5.3_15887"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.20689908835e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
494	"Qld_RE_DomE_12.5.3_15911"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.81293017935e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
495	"Qld_RE_DomE_12.5.3_15917"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
496	"Qld_RE_DomE_12.5.3_15921"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
497	"Qld_RE_DomE_12.5.3_15923"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.92264221436e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
498	"Qld_RE_DomE_12.5.3_15930"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.78409468952e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
499	"Qld_RE_DomE_12.5.3_15933"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.06936232716e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
500	"Qld_RE_DomE_12.5.3_15938"	"12.5.3"	"12.5.3"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.70856010834e-03	"RE_12.5.3"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
506	"Qld_RE_DomE_12.5.3a_15983"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
507	"Qld_RE_DomE_12.5.3a_16007"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
508	"Qld_RE_DomE_12.5.3a_16008"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
509	"Qld_RE_DomE_12.5.3a_16018"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	2.32236045444e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
510	"Qld_RE_DomE_12.5.3a_16022"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.17296680676e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
511	"Qld_RE_DomE_12.5.3a_16024"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.52803795712e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
512	"Qld_RE_DomE_12.5.3a_16033"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.1914664649e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
513	"Qld_RE_DomE_12.5.3a_16036"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.2"	"70/30"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.88033350418e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
514	"Qld_RE_DomE_12.5.3a_16043"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	5.22966961208e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
515	"Qld_RE_DomE_12.5.3a_16049"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	4.76349779942e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
516	"Qld_RE_DomE_12.5.3a_16061"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
517	"Qld_RE_DomE_12.5.3a_16062"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	6.36483012316e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
518	"Qld_RE_DomE_12.5.3a_16064"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	5.08795989296e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
519	"Qld_RE_DomE_12.5.3a_16075"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	5.92653428134e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
520	"Qld_RE_DomE_12.5.3a_16076"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	4.50130617984e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
521	"Qld_RE_DomE_12.5.3a_16078"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.2"	"70/30"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
522	"Qld_RE_DomE_12.5.3a_16082"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.64311022719e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
523	"Qld_RE_DomE_12.5.3a_16090"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	3.40618834765e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
524	"Qld_RE_DomE_12.5.3a_16093"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.2795004264e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
525	"Qld_RE_DomE_12.5.3a_16103"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.89980974141e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
531	"Qld_RE_DomE_12.5.3a_16117"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.5.3/12.5.1"	"70/30"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"70/30"	"9g"	"9"	"3"	5.44892751166e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
543	"Qld_RE_DomE_12.5.3a_16177"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
544	"Qld_RE_DomE_12.5.3a_16188"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.97005445987e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
545	"Qld_RE_DomE_12.5.3a_16189"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.93568378811e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
546	"Qld_RE_DomE_12.5.3a_16197"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.01665422789e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
552	"Qld_RE_DomE_12.5.3a_16227"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.47819517003e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
553	"Qld_RE_DomE_12.5.3a_16228"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	8.15960048601e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
554	"Qld_RE_DomE_12.5.3a_16232"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.14913105569e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
555	"Qld_RE_DomE_12.5.3a_16234"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.5.3/12.5.1"	"90/10"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"90/10"	"9g"	"9"	"3"	4.89343207203e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
556	"Qld_RE_DomE_12.5.3a_16237"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.59459384127e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
557	"Qld_RE_DomE_12.5.3a_16245"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	2.05661027186e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
558	"Qld_RE_DomE_12.5.3a_16249"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.82881569427e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
559	"Qld_RE_DomE_12.5.3a_16251"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	5.36441202544e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
560	"Qld_RE_DomE_12.5.3a_16253"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.91115466229e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
561	"Qld_RE_DomE_12.5.3a_16254"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.5.3/12.5.1"	"90/10"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"90/10"	"9g"	"9"	"3"	5.27539891667e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
562	"Qld_RE_DomE_12.5.3a_16259"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	1.96329203568e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
563	"Qld_RE_DomE_12.5.3a_16260"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.9774126377e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
564	"Qld_RE_DomE_12.5.3a_16261"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.83348816933e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
565	"Qld_RE_DomE_12.5.3a_16267"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	8.48116264269e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
566	"Qld_RE_DomE_12.5.3a_16268"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.5.3/12.5.1"	"90/10"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"90/10"	"9g"	"9"	"3"	4.30704474979e-03	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
567	"Qld_RE_DomE_12.5.3a_16271"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
568	"Qld_RE_DomE_12.5.3a_16273"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	8.89584897131e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
569	"Qld_RE_DomE_12.5.3a_16275"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.93458718882e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
570	"Qld_RE_DomE_12.5.3a_16286"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.10752813073e-03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
571	"Qld_RE_DomE_12.5.3a_16297"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.03935800942e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
572	"Qld_RE_DomE_12.5.3a_16298"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.99758708507e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
573	"Qld_RE_DomE_12.5.3a_16304"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.35186621139e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
574	"Qld_RE_DomE_12.5.3a_16309"	"12.5.3a/12.5.2a"	"12.5.3a"	"12.5.2a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.5.3/12.5.2"	"60/40"	"5"	"E/E"	254	"E/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.03	"RE_12.5.3a/12.5.2a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
575	"Qld_RE_DomE_12.5.3a_16318"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
576	"Qld_RE_DomE_12.5.3a_16320"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.7075294913e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
577	"Qld_RE_DomE_12.5.3a_16327"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.64962208014e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
590	"Qld_RE_DomE_12.5.3a_16373"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.52667204392e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
591	"Qld_RE_DomE_12.5.3a_16383"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	7.36268824986e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
592	"Qld_RE_DomE_12.5.3a_16386"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.14670278291e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
593	"Qld_RE_DomE_12.5.3a_16389"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	3.95445119615e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
594	"Qld_RE_DomE_12.5.3a_16390"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	5.18384503365e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
595	"Qld_RE_DomE_12.5.3a_16391"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
602	"Qld_RE_DomE_12.5.3a_16425"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	4.56098046359e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
603	"Qld_RE_DomE_12.5.3a_16445"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	8.55007745722e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
604	"Qld_RE_DomE_12.5.3a_16446"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.5.3/12.5.1"	"90/10"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"90/10"	"9g"	"9"	"3"	0.01	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
605	"Qld_RE_DomE_12.5.3a_16451"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.02	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
606	"Qld_RE_DomE_12.5.3a_16470"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	9.02373968389e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
607	"Qld_RE_DomE_12.5.3a_16471"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	2.14218781178e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
608	"Qld_RE_DomE_12.5.3a_16473"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	5.72522554262e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
609	"Qld_RE_DomE_12.5.3a_16474"	"12.5.3a/12.5.1"	"12.5.3a"	"12.5.1"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.5.3/12.5.1"	"90/10"	"5"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g/10b"	"90/10"	"9g"	"9"	"3"	0.02	"RE_12.5.3a/12.5.1"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
610	"Qld_RE_DomE_12.5.3a_16484"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	2.94629443744e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
611	"Qld_RE_DomE_12.5.3a_16486"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	6.09419398291e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
612	"Qld_RE_DomE_12.5.3a_16488"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	4.82588337326e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
613	"Qld_RE_DomE_12.5.3a_16492"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
614	"Qld_RE_DomE_12.5.3a_16495"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	3.39687334712e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
615	"Qld_RE_DomE_12.5.3a_16497"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	5.45190227468e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
616	"Qld_RE_DomE_12.5.3a_16510"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
617	"Qld_RE_DomE_12.5.3a_16514"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	4.87102736162e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
618	"Qld_RE_DomE_12.5.3a_16516"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	6.22276453911e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
619	"Qld_RE_DomE_12.5.3a_16523"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9g"	"100"	"9g"	"9"	"3"	0.02	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
620	"Qld_RE_DomE_12.5.3a_16524"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	9.4697346251e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
621	"Qld_RE_DomE_12.5.3a_16548"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	0.08	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
622	"Qld_RE_DomE_12.5.3a_16590"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	4.2155453757e-03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
623	"Qld_RE_DomE_12.5.3a_16598"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	0.01	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
624	"Qld_RE_DomE_12.5.3a_16612"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	0.03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
625	"Qld_RE_DomE_12.5.3a_16615"	"12.5.3a"	"12.5.3a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.5.3"	"100"	"5"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9g"	"100"	"9g"	"9"	"3"	0.03	"RE_12.5.3a"	"12.5.3"	120503.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus racemosa subsp. racemosa woodland with Corymbia intermedia, E. siderophloia +/- E. tindaliae, E. resinifera, E. pilularis, E. microcorys, Angophora leiocarpa. Melaleuca quinquenervia is often a prominent feature of lower slopes. Minor patches (<1ha) dominated by Corymbia citriodora subsp. variegata sometimes occur. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)
 Vegetation communities in this regional ecosystem include: 
12.5.3a:  Corymbia intermedia, Eucalyptus seeana +/- E. racemosa subsp. racemosa, Angophora leiocarpa, E. siderophloia, C. citriodora subsp. variegata, Lophostemon suaveolens open woodland. Occurs on complex of remnant Tertiary surfaces +/- Cainozoic and Mesozoic sediments. (BVG1M: 9g)"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Eucalyptus racemosa woodland on remnant Tertiary surfaces"	"Ryan, T.S. (ed.) (2012); Bean et al. (1998), D8a, H14"	"4, 2, (9), (3)"	"Glass House Mountains NP, Tewantin NP (R), Tewantin NP, Freshwater NP, Great Sandy NP, Noosa NP, Sheep Station Creek CP, Teerk Roo Ra NP (IJMA), Harry Spring CP, Springwood CP, [Ningi Creek CP], [Pumicestone NP], [Teerk Roo Ra CP (IJMA)]"		"SEASON: Late summer to winter. INTENSITY: Low to moderate. INTERVAL: 7-25 years. STRATEGY: Aim for a burn mosaic of 40-60% over the burn area. A diversity of season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics. Late summer burns assist with maintaining control of fire intensity. ISSUES: Avoid repeated low intensity fires. Fires that are too frequent will eliminate obligate seeding species. Fire frequency should be such as to allow trees to reach maturity and produce viable seed."	"12.5.3: Occurs from Noosa southward. Extensively cleared for exotic pine plantation, horticulture and urban development. Patches of this vegetation >2ha in size occurring on Cainozoic to Proterozoic sediments are defined as 12.9-10.4.
12.5.3a: Occurs mainly to the south of Brisbane. Extensively cleared for urban development. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this floristic association on Cainozoic to Proterozoic sediments that are mappable (>2ha) are defined as 12.9-10.12."		12.00	5.00		"Mid-dense"	"OF"	"9g"
626	"Qld_RE_DomE_12.8.21_16272"	"12.8.21"	"12.8.21"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.21"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a"	"100"	"7a"	"7"	"1"	0.10	"RE_12.8.21"	"12.8.21"	120821.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Low microphyll vine forest and semi-evergreen vine thicket +/- Araucaria cunninghamii. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic igneous rocks, especially basalt. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on Cainozoic igneous rocks. Usually southern half of bioregion"	"Semi-evergreen vine thicket with Brachychiton rupestris on Cainozoic igneous rocks. Usually southern half of bioregion"	"Bean et al. (1998), G7 (in part)"	"6, 2, 5, (1)"	"Bunya Mountains NP, Woroon NP, Nangur NP, Dwyers Scrub CP, Main Range NP, Boat Mountain CP 2, Boat Mountain CP 1, [Flagstone Creek CP]"	"Habitat for near threatened flora species including Callitris baileyi and Cryptocarya floydii."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Confined to south of bioregion. Lockyer Valley and Bunya Mountains. Remnants require intensive management because of invasion by weeds and fire damage on margins."		12.00	8.00	"Contains riverine wetland."	"Dense"	"CF"	"7a"
627	"Qld_RE_DomE_12.8.23_16341"	"12.8.23"	"12.8.23"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.23"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"25a"	"100"	"25a"	"25"	"10"	0.01	"RE_12.8.23"	"12.8.23"	120823.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Acacia harpophylla +/- semi-evergreen vine thicket species +/- Casuarina cristata +/- Eucalyptus populnea tall open forest. Occurs on Cainozoic igneous rocks, especially basalt. (BVG1M: 25a)"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Bean et al. (1998), H1 (in part), H47"	"6, 5, 2, (7), (10), (1)"	"[Bunya Mountains NP]"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Cleared for pasture and cropping. Melaleuca bracteata conspicuous along associated watercourses."		12.00	8.00		"Mid-dense"	"OF"	"25a"
628	"Qld_RE_DomE_12.8.23_16384"	"12.8.23"	"12.8.23"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.23"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"25a"	"100"	"25a"	"25"	"10"	8.95686012619e-03	"RE_12.8.23"	"12.8.23"	120823.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Acacia harpophylla +/- semi-evergreen vine thicket species +/- Casuarina cristata +/- Eucalyptus populnea tall open forest. Occurs on Cainozoic igneous rocks, especially basalt. (BVG1M: 25a)"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Bean et al. (1998), H1 (in part), H47"	"6, 5, 2, (7), (10), (1)"	"[Bunya Mountains NP]"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Cleared for pasture and cropping. Melaleuca bracteata conspicuous along associated watercourses."		12.00	8.00		"Mid-dense"	"OF"	"25a"
629	"Qld_RE_DomE_12.8.23_18467"	"12.8.23"	"12.8.23"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.23"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.8520159117e-03	"RE_12.8.23"	"12.8.23"	120823.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Acacia harpophylla +/- semi-evergreen vine thicket species +/- Casuarina cristata +/- Eucalyptus populnea tall open forest. Occurs on Cainozoic igneous rocks, especially basalt. (BVG1M: 25a)"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Bean et al. (1998), H1 (in part), H47"	"6, 5, 2, (7), (10), (1)"	"[Bunya Mountains NP]"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Cleared for pasture and cropping. Melaleuca bracteata conspicuous along associated watercourses."		12.00	8.00		"Mid-dense"	"OF"	"25a"
630	"Qld_RE_DomE_12.8.23_18500"	"12.8.23"	"12.8.23"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.23"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	6.0415543833e-03	"RE_12.8.23"	"12.8.23"	120823.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Acacia harpophylla +/- semi-evergreen vine thicket species +/- Casuarina cristata +/- Eucalyptus populnea tall open forest. Occurs on Cainozoic igneous rocks, especially basalt. (BVG1M: 25a)"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Bean et al. (1998), H1 (in part), H47"	"6, 5, 2, (7), (10), (1)"	"[Bunya Mountains NP]"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Cleared for pasture and cropping. Melaleuca bracteata conspicuous along associated watercourses."		12.00	8.00		"Mid-dense"	"OF"	"25a"
631	"Qld_RE_DomE_12.8.23_18508"	"12.8.23"	"12.8.23"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.23"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	8.34505103252e-03	"RE_12.8.23"	"12.8.23"	120823.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Acacia harpophylla +/- semi-evergreen vine thicket species +/- Casuarina cristata +/- Eucalyptus populnea tall open forest. Occurs on Cainozoic igneous rocks, especially basalt. (BVG1M: 25a)"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Acacia harpophylla open forest on Cainozoic igneous rocks"	"Bean et al. (1998), H1 (in part), H47"	"6, 5, 2, (7), (10), (1)"	"[Bunya Mountains NP]"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Cleared for pasture and cropping. Melaleuca bracteata conspicuous along associated watercourses."		12.00	8.00		"Mid-dense"	"OF"	"25a"
632	"Qld_RE_DomE_12.8.24_16767"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.02	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
633	"Qld_RE_DomE_12.8.24_16817"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
634	"Qld_RE_DomE_12.8.24_16832"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
635	"Qld_RE_DomE_12.8.24_17067"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
636	"Qld_RE_DomE_12.8.24_17080"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
637	"Qld_RE_DomE_12.8.24_17501"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
638	"Qld_RE_DomE_12.8.24_17623"	"12.8.24/12.8.20"	"12.8.24"	"12.8.20"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.8.24/12.8.20"	"70/30"	"8"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b/9a"	"70/30"	"10b"	"10"	"3"	0.04	"RE_12.8.24/12.8.20"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
639	"Qld_RE_DomE_12.8.24_17680"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	9.82425236941e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
640	"Qld_RE_DomE_12.8.24_17695"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
641	"Qld_RE_DomE_12.8.24_17711"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	8.4342660199e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
642	"Qld_RE_DomE_12.8.24_17745"	"12.8.24/12.8.9"	"12.8.24"	"12.8.9"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.8.24/12.8.9"	"90/10"	"8"	"E/OC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b/8a"	"90/10"	"10b"	"10"	"3"	0.15	"RE_12.8.24/12.8.9"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
643	"Qld_RE_DomE_12.8.24_17778"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.05	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
644	"Qld_RE_DomE_12.8.24_17780"	"12.8.24/12.8.16"	"12.8.24"	"12.8.16"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.8.24/12.8.16"	"70/30"	"8"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b/11a"	"70/30"	"10b"	"10"	"3"	0.01	"RE_12.8.24/12.8.16"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
645	"Qld_RE_DomE_12.8.24_17794"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.08	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
651	"Qld_RE_DomE_12.8.24_17913"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.02	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
652	"Qld_RE_DomE_12.8.24_17914"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
653	"Qld_RE_DomE_12.8.24_17942"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	6.08768438633e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
654	"Qld_RE_DomE_12.8.24_18076"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.02	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
655	"Qld_RE_DomE_12.8.24_18279"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
1155	"Qld_RE_DomE_12.9-10.15_18104"	"12.9-10.15/12.9-10.17"	"12.9-10.15"	"12.9-10.17"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.9-10.15/12.9-10.17"	"95/5"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a/9a"	"95/5"	"7a"	"7"	"1"	0.01	"RE_12.9-10.15/12.9-10.17"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1156	"Qld_RE_DomE_12.9-10.15_18112"	"12.9-10.15/12.9-10.17"	"12.9-10.15"	"12.9-10.17"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.9-10.15/12.9-10.17"	"95/5"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a/9a"	"95/5"	"7a"	"7"	"1"	0.02	"RE_12.9-10.15/12.9-10.17"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1157	"Qld_RE_DomE_12.9-10.15_18200"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"7a"	"100"	"7a"	"7"	"1"	3.52342175721e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1158	"Qld_RE_DomE_12.9-10.15_18600"	"12.9-10.15/12.9-10.16/12.9-10.6"	"12.9-10.15"	"12.9-10.16"	"12.9-10.6"	" "	" "	"40/30/30"	40	30	30	0	0	"12.9-10.15/12.9-10.16/12.9-10.6"	"40/30/30"	"9-10"	"E/E/E"	254	"E/O/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"7a/5a/25a"	"40/30/30"	"7a"	"7"	"1"	5.66451605229e-03	"RE_12.9-10.15/12.9-10.16/12.9-10.6"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
857	"Qld_RE_DomE_12.9-10.11a_17892"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.12575587715e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
858	"Qld_RE_DomE_12.9-10.11a_17925"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
859	"Qld_RE_DomE_12.9-10.11a_17934"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.86226771334e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
860	"Qld_RE_DomE_12.9-10.11a_17968"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.06307739831e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
861	"Qld_RE_DomE_12.9-10.11a_17971"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.73405135471e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
999	"Qld_RE_DomE_12.9-10.12_17235"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1000	"Qld_RE_DomE_12.9-10.12_17240"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	4.71395781239e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1001	"Qld_RE_DomE_12.9-10.12_17246"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.91392686319e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1002	"Qld_RE_DomE_12.9-10.12_17248"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.48032365621e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1003	"Qld_RE_DomE_12.9-10.12_17249"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1024	"Qld_RE_DomE_12.9-10.12_17346"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1025	"Qld_RE_DomE_12.9-10.12_17347"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.34755424008e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1026	"Qld_RE_DomE_12.9-10.12_17350"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.7"	"60/40"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"60/40"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1027	"Qld_RE_DomE_12.9-10.12_17363"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.52666092854e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1167	"Qld_RE_DomE_12.9-10.15_18871"	"12.9-10.15/12.9-10.16"	"12.9-10.15"	"12.9-10.16"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.15/12.9-10.16"	"80/20"	"9-10"	"E/E"	254	"E/O"	67	"E-dom"	"8.0"	50	"B"	"A"	"7a/5a"	"80/20"	"7a"	"7"	"1"	0.02	"RE_12.9-10.15/12.9-10.16"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1168	"Qld_RE_DomE_12.9-10.16_17621"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	6.42582846531e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1169	"Qld_RE_DomE_12.9-10.16_17647"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	2.97606905735e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1170	"Qld_RE_DomE_12.9-10.16_17684"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1210	"Qld_RE_DomE_12.9-10.16_19255"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1211	"Qld_RE_DomE_12.9-10.16_19256"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1212	"Qld_RE_DomE_12.9-10.16_19263"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1213	"Qld_RE_DomE_12.9-10.16_19268"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1214	"Qld_RE_DomE_12.9-10.16_19269"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
656	"Qld_RE_DomE_12.8.24_18330"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
657	"Qld_RE_DomE_12.8.24_18335"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
658	"Qld_RE_DomE_12.8.24_18388"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	7.58757949888e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
659	"Qld_RE_DomE_12.8.24_18389"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
660	"Qld_RE_DomE_12.8.24_18409"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.02	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
661	"Qld_RE_DomE_12.8.24_18451"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
662	"Qld_RE_DomE_12.8.24_18464"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	3.67851679489e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
663	"Qld_RE_DomE_12.8.24_18486"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	6.19656033321e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
664	"Qld_RE_DomE_12.8.24_18497"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	6.43002937195e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
665	"Qld_RE_DomE_12.8.24_18507"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
666	"Qld_RE_DomE_12.8.24_18519"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.02	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
667	"Qld_RE_DomE_12.8.24_18535"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
668	"Qld_RE_DomE_12.8.24_18566"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	5.3296861054e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
669	"Qld_RE_DomE_12.8.24_18568"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
670	"Qld_RE_DomE_12.8.24_18570"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
681	"Qld_RE_DomE_12.8.24_18694"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
682	"Qld_RE_DomE_12.8.24_18750"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	7.33130549187e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
683	"Qld_RE_DomE_12.8.24_18765"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	9.39659458418e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
684	"Qld_RE_DomE_12.8.24_18775"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	6.17770089843e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
685	"Qld_RE_DomE_12.8.24_18776"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.02	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
691	"Qld_RE_DomE_12.8.24_18841"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
692	"Qld_RE_DomE_12.8.24_18852"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	7.02830269672e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
693	"Qld_RE_DomE_12.8.24_18856"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.06	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
694	"Qld_RE_DomE_12.8.24_18878"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	6.92319417477e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
695	"Qld_RE_DomE_12.8.24_18994"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	7.07305105079e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
696	"Qld_RE_DomE_12.8.24_19006"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
697	"Qld_RE_DomE_12.8.24_19009"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	6.99472345362e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
698	"Qld_RE_DomE_12.8.24_19010"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	6.58662719045e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
699	"Qld_RE_DomE_12.8.24_19015"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	9.42198255097e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
700	"Qld_RE_DomE_12.8.24_19037"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
701	"Qld_RE_DomE_12.8.24_19064"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	7.98273582432e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
702	"Qld_RE_DomE_12.8.24_19091"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
703	"Qld_RE_DomE_12.8.24_19171"	"12.8.24/12.8.16"	"12.8.24"	"12.8.16"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.8.24/12.8.16"	"60/40"	"8"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b/11a"	"60/40"	"10b"	"10"	"3"	0.15	"RE_12.8.24/12.8.16"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
704	"Qld_RE_DomE_12.8.24_19179"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	6.05830161338e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
705	"Qld_RE_DomE_12.8.24_19208"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
706	"Qld_RE_DomE_12.8.24_19210"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.07	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
707	"Qld_RE_DomE_12.8.24_19221"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.07	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
708	"Qld_RE_DomE_12.8.24_19223"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
709	"Qld_RE_DomE_12.8.24_19239"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.02	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
710	"Qld_RE_DomE_12.8.24_19246"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	8.96925679345e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
711	"Qld_RE_DomE_12.8.24_19252"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	9.79990977703e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
712	"Qld_RE_DomE_12.8.24_19261"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.02	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
713	"Qld_RE_DomE_12.8.24_19264"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
714	"Qld_RE_DomE_12.8.24_19336"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
715	"Qld_RE_DomE_12.8.24_19351"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
726	"Qld_RE_DomE_12.8.24_19474"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	5.40274946711e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
727	"Qld_RE_DomE_12.8.24_19475"	"12.8.24/12.8.16"	"12.8.24"	"12.8.16"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.8.24/12.8.16"	"70/30"	"8"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b/11a"	"70/30"	"10b"	"10"	"3"	0.03	"RE_12.8.24/12.8.16"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
728	"Qld_RE_DomE_12.8.24_19479"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.01	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
729	"Qld_RE_DomE_12.8.24_19487"	"12.8.24/12.8.16"	"12.8.24"	"12.8.16"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.8.24/12.8.16"	"70/30"	"8"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b/11a"	"70/30"	"10b"	"10"	"3"	0.03	"RE_12.8.24/12.8.16"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
730	"Qld_RE_DomE_12.8.24_19488"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.08	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
916	"Qld_RE_DomE_12.9-10.12_16582"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.04	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
917	"Qld_RE_DomE_12.9-10.12_16585"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
918	"Qld_RE_DomE_12.9-10.12_16591"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.36161924902e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
919	"Qld_RE_DomE_12.9-10.12_16595"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	9.3894087307e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
920	"Qld_RE_DomE_12.9-10.12_16607"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	9.84350756651e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1219	"Qld_RE_DomE_12.9-10.16_19338"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1220	"Qld_RE_DomE_12.9-10.16_19352"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1221	"Qld_RE_DomE_12.9-10.16_19353"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1222	"Qld_RE_DomE_12.9-10.16_19369"	"12.9-10.16/12.8.4"	"12.9-10.16"	"12.8.4"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.16/12.8.4"	"70/30"	"9-10"	"E/NC"	254	"O/L"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a/2a"	"70/30"	"5a"	"5"	"1"	5.51065579097e-03	"RE_12.9-10.16/12.8.4"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
731	"Qld_RE_DomE_12.8.24_19490"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	0.03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
737	"Qld_RE_DomE_12.8.24_19555"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"10b"	"100"	"10b"	"10"	"3"	8.23189369869e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
738	"Qld_RE_DomE_12.8.24_19574"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"10b"	"100"	"10b"	"10"	"3"	9.38609092183e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
739	"Qld_RE_DomE_12.8.24_19615"	"12.8.24"	"12.8.24"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.8.24"	"100"	"8"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"10b"	"100"	"10b"	"10"	"3"	4.84646660066e-03	"RE_12.8.24"	"12.8.24"	120824.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Medium"	"Corymbia citriodora subsp. variegata, Eucalyptus crebra +/- E. moluccana open forest. Occurs on Cainozoic igneous rocks especially lower slopes of rhyolite and trachyte hills (e.g. Moogerah Peaks). (BVG1M: 10b)"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Corymbia citriodora subsp. variegata open forest on Cainozoic igneous rocks especially trachyte"	"Bean et al. (1998), H19 (in part)"	"2, 1, 5, 7, (6)"	"Mount Barney NP, Flinders Peak CP, Mount Binga NP, Moogerah Peaks NP, Tamborine NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."			12.00	8.00		"Mid-dense"	"OF"	"10b"
740	"Qld_RE_DomE_12.9-10.11_16246"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.5738780833e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
741	"Qld_RE_DomE_12.9-10.11_16867"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
742	"Qld_RE_DomE_12.9-10.11_16921"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
743	"Qld_RE_DomE_12.9-10.11_16957"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.90243526913e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
744	"Qld_RE_DomE_12.9-10.11_16970"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.75564788192e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
745	"Qld_RE_DomE_12.9-10.11_17068"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.56440496316e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
746	"Qld_RE_DomE_12.9-10.11_17112"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
747	"Qld_RE_DomE_12.9-10.11_17129"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.73753719145e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
748	"Qld_RE_DomE_12.9-10.11_17133"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.32217995628e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
749	"Qld_RE_DomE_12.9-10.11_17135"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.91094756873e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
750	"Qld_RE_DomE_12.9-10.11_17154"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.02	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
751	"Qld_RE_DomE_12.9-10.11_17208"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
752	"Qld_RE_DomE_12.9-10.11_17214"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.47102372643e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
753	"Qld_RE_DomE_12.9-10.11_17224"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.53151948747e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
754	"Qld_RE_DomE_12.9-10.11_17227"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.67976470397e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
755	"Qld_RE_DomE_12.9-10.11_17233"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.59119638071e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
756	"Qld_RE_DomE_12.9-10.11_17234"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
757	"Qld_RE_DomE_12.9-10.11_17237"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	8.73516771096e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
758	"Qld_RE_DomE_12.9-10.11_17247"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.56622886568e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
759	"Qld_RE_DomE_12.9-10.11_17255"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.39254795397e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
760	"Qld_RE_DomE_12.9-10.11_17256"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.59226273581e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
761	"Qld_RE_DomE_12.9-10.11_17258"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.8816420968e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
772	"Qld_RE_DomE_12.9-10.11_17415"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.10301389816e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
773	"Qld_RE_DomE_12.9-10.11_17532"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
774	"Qld_RE_DomE_12.9-10.11_17551"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.34588669415e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
775	"Qld_RE_DomE_12.9-10.11_17560"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
776	"Qld_RE_DomE_12.9-10.11_17574"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	9.56343980665e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
782	"Qld_RE_DomE_12.9-10.11_17900"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.70570765237e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
783	"Qld_RE_DomE_12.9-10.11_18002"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.31183723988e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
784	"Qld_RE_DomE_12.9-10.11_18008"	"12.9-10.11"	"12.9-10.11"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	1.89728133476e-03	"RE_12.9-10.11"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
785	"Qld_RE_DomE_12.9-10.11a_16787"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.34765437861e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
786	"Qld_RE_DomE_12.9-10.11a_16818"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.70949859954e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
787	"Qld_RE_DomE_12.9-10.11a_16830"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.01002708811e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
788	"Qld_RE_DomE_12.9-10.11a_16859"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	8.02126298526e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
789	"Qld_RE_DomE_12.9-10.11a_16896"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	8.7552898585e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
790	"Qld_RE_DomE_12.9-10.11a_16898"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
791	"Qld_RE_DomE_12.9-10.11a_16938"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.09894311648e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
792	"Qld_RE_DomE_12.9-10.11a_16959"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.02	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
793	"Qld_RE_DomE_12.9-10.11a_16963"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.40683647007e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
794	"Qld_RE_DomE_12.9-10.11a_16972"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.31250889342e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
795	"Qld_RE_DomE_12.9-10.11a_16983"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.3970604869e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
796	"Qld_RE_DomE_12.9-10.11a_16988"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.24476818192e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
797	"Qld_RE_DomE_12.9-10.11a_16999"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.08644776281e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
798	"Qld_RE_DomE_12.9-10.11a_17009"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.73178093244e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
799	"Qld_RE_DomE_12.9-10.11a_17016"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
800	"Qld_RE_DomE_12.9-10.11a_17038"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.63484029832e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
801	"Qld_RE_DomE_12.9-10.11a_17045"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	8.88481312777e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
802	"Qld_RE_DomE_12.9-10.11a_17053"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.02	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
803	"Qld_RE_DomE_12.9-10.11a_17054"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.17807893999e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
804	"Qld_RE_DomE_12.9-10.11a_17071"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.02	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
805	"Qld_RE_DomE_12.9-10.11a_17073"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.23966059861e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
806	"Qld_RE_DomE_12.9-10.11a_17086"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.71853731636e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
812	"Qld_RE_DomE_12.9-10.11a_17114"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
813	"Qld_RE_DomE_12.9-10.11a_17119"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
814	"Qld_RE_DomE_12.9-10.11a_17124"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.81433171056e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
815	"Qld_RE_DomE_12.9-10.11a_17128"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.57642275412e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
816	"Qld_RE_DomE_12.9-10.11a_17137"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.74758628873e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
817	"Qld_RE_DomE_12.9-10.11a_17143"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.02	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
818	"Qld_RE_DomE_12.9-10.11a_17156"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.88964147686e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
819	"Qld_RE_DomE_12.9-10.11a_17182"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.89508136053e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
820	"Qld_RE_DomE_12.9-10.11a_17197"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.10776283749e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
821	"Qld_RE_DomE_12.9-10.11a_17205"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.08	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
822	"Qld_RE_DomE_12.9-10.11a_17211"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
823	"Qld_RE_DomE_12.9-10.11a_17213"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.04	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
824	"Qld_RE_DomE_12.9-10.11a_17215"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.22474938543e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
825	"Qld_RE_DomE_12.9-10.11a_17219"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.9245346477e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
826	"Qld_RE_DomE_12.9-10.11a_17229"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.15995924871e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
827	"Qld_RE_DomE_12.9-10.11a_17230"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.11822946649e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
828	"Qld_RE_DomE_12.9-10.11a_17257"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.50265285348e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
829	"Qld_RE_DomE_12.9-10.11a_17260"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.02	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
830	"Qld_RE_DomE_12.9-10.11a_17265"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.37994736271e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
831	"Qld_RE_DomE_12.9-10.11a_17291"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
832	"Qld_RE_DomE_12.9-10.11a_17294"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
833	"Qld_RE_DomE_12.9-10.11a_17299"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
834	"Qld_RE_DomE_12.9-10.11a_17321"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
835	"Qld_RE_DomE_12.9-10.11a_17330"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
836	"Qld_RE_DomE_12.9-10.11a_17334"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.67393956266e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
837	"Qld_RE_DomE_12.9-10.11a_17348"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.6972927187e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
838	"Qld_RE_DomE_12.9-10.11a_17367"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.17450540973e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
839	"Qld_RE_DomE_12.9-10.11a_17534"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
840	"Qld_RE_DomE_12.9-10.11a_17541"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.27576974507e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
841	"Qld_RE_DomE_12.9-10.11a_17548"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"21b"	"100"	"21b"	"21"	"8"	0.01	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
842	"Qld_RE_DomE_12.9-10.11a_17643"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.98424321555e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
843	"Qld_RE_DomE_12.9-10.11a_17656"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.01073011241e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
844	"Qld_RE_DomE_12.9-10.11a_17665"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.23530740117e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
845	"Qld_RE_DomE_12.9-10.11a_17779"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.89038666497e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
846	"Qld_RE_DomE_12.9-10.11a_17795"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.18454421267e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
847	"Qld_RE_DomE_12.9-10.11a_17797"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.16495145024e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
848	"Qld_RE_DomE_12.9-10.11a_17812"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.74965871065e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
849	"Qld_RE_DomE_12.9-10.11a_17819"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.84923860841e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
850	"Qld_RE_DomE_12.9-10.11a_17856"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.20639926312e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
851	"Qld_RE_DomE_12.9-10.11a_17870"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	7.71469551079e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
852	"Qld_RE_DomE_12.9-10.11a_17873"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	8.9345747539e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
853	"Qld_RE_DomE_12.9-10.11a_17888"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.63793311279e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
854	"Qld_RE_DomE_12.9-10.11a_17889"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.86075104742e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
855	"Qld_RE_DomE_12.9-10.11a_17890"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.36993875911e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
856	"Qld_RE_DomE_12.9-10.11a_17891"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.77516008246e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
862	"Qld_RE_DomE_12.9-10.11a_17973"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.98709929225e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
863	"Qld_RE_DomE_12.9-10.11a_17979"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	1.81263206316e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
864	"Qld_RE_DomE_12.9-10.11a_17991"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.92457054271e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
865	"Qld_RE_DomE_12.9-10.11a_18000"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.58916754225e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
866	"Qld_RE_DomE_12.9-10.11a_18001"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.28876413217e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
867	"Qld_RE_DomE_12.9-10.11a_18003"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	6.92192361409e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
868	"Qld_RE_DomE_12.9-10.11a_18004"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.72746287966e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
869	"Qld_RE_DomE_12.9-10.11a_18017"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.60739969903e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
870	"Qld_RE_DomE_12.9-10.11a_18023"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	2.49067203009e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
871	"Qld_RE_DomE_12.9-10.11a_18025"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	5.74729031218e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
872	"Qld_RE_DomE_12.9-10.11a_18029"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.00484695995e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
873	"Qld_RE_DomE_12.9-10.11a_18031"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.66839442372e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
874	"Qld_RE_DomE_12.9-10.11a_18033"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.08415987617e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
875	"Qld_RE_DomE_12.9-10.11a_18035"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	3.95348173302e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
876	"Qld_RE_DomE_12.9-10.11a_18041"	"12.9-10.11a"	"12.9-10.11a"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.11"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"21b"	"100"	"21b"	"21"	"8"	4.62997862113e-03	"RE_12.9-10.11a"	"12.9-10.11"	120911.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Melaleuca irbyana low open forest or thicket. Emergent Eucalyptus moluccana, E. crebra, E. tereticornis or Corymbia citriodora subsp. variegata may be present. Occurs on Mesozoic sediments where drainage of soils is impeded. (BVG1M: 21b)
 Vegetation communities in this regional ecosystem include: 
12.9-10.11a:  Corymbia citriodora subsp. variegata, Eucalyptus crebra and/or E. moluccana, E. tereticornis, E. crebra open forest with a sparse to mid-dense understorey of Melaleuca irbyana. Occurs on lower slopes and elevated flats with impeded drainage on Mesozoic sediments. (BVG1M: 21b)"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Melaleuca irbyana low open forest on sedimentary rocks"	"Bean et al. (1998), C5"	"2"	"No representation"	"Habitat for threatened flora species including Melaleuca irbyana.
12.9-10.11a: Habitat for threatened flora species including Melaleuca irbyana."	"SEASON: Late summer to mid-winter (after rain). INTENSITY: Planned and occasional unplanned burns (typically of higher intensity) influence the ecology of melaleuca ecosystems. INTERVAL: Mixed grass/shrub 6-20 years. STRATEGY: Aim for a 25-70% burn mosaic (in association with surrounding ecosystems, as melaleuca ecosystems often just occur in patches or along natural drainage lines). Fires may, depending on the conditions and type of vegetation, burn areas larger than just the melaleuca ecosystem. Ensure secure boundaries from non fire-regime adapted ecosystems. High soil moisture (or presence of water on the ground) is required, as avoidance of peat-type fires must be maintained. ISSUES: M. irbyana may be managed differently to the rest. This is a low melaleuca forest with eucalypt overstorey. Fire regimes for melaleuca ecosystems in general require further fire research. Melaleuca forests are fire-adapted, but too high an intensity or frequent fire will slow or prevent regeneration and lead to lower species richness (since these communities contain numerous obligate seed regenerating species that require sufficient fire intervals to produce seed). High intensity fires may kill trees and lead to whipstick regeneration. Too frequent fire may result in a net loss of nutrients over time from an already nutrient poor system. Fire associations are significantly influenced by understorey composition. Mixed understorey communities burn in a similar way to dry sclerophyll, in association with the surrounding dry sclerophyll, though somewhat less frequently due to the additional moisture present in melaleuca communities."	"12.9-10.11: Restricted to Moreton Basin around Morton Vale, Calvert to Harrisville and Jimboomba. Being cleared for rural residential development and pasture production. This floristic association on land zone 3 is mapped as 12.3.3c.
12.9-10.11a: Restricted to Moreton Basin around Ipswich and Jimboomba. Being cleared for rural residential development. Generally the Melaleuca irbyana understorey ranges from sparse when associated with C. citriodora subsp. variegata and E. crebra to mid-dense when associated with E. moluccana & E. tereticornis. This floristic association on land zone 3 is mapped as 12.3.3b veg (C5a)."		12.00	9.00		"Mid-dense"	"LOF"	"21b"
881	"Qld_RE_DomE_12.9-10.12_16289"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	0.03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
882	"Qld_RE_DomE_12.9-10.12_16335"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	8.38468372907e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
883	"Qld_RE_DomE_12.9-10.12_16346"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	2.06689665422e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
888	"Qld_RE_DomE_12.9-10.12_16397"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
889	"Qld_RE_DomE_12.9-10.12_16401"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
890	"Qld_RE_DomE_12.9-10.12_16407"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	3.00312843233e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
891	"Qld_RE_DomE_12.9-10.12_16414"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
892	"Qld_RE_DomE_12.9-10.12_16419"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.04954192593e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
893	"Qld_RE_DomE_12.9-10.12_16427"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.7957427063e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
894	"Qld_RE_DomE_12.9-10.12_16432"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	6.95772450532e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
895	"Qld_RE_DomE_12.9-10.12_16450"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	3.49144047896e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
896	"Qld_RE_DomE_12.9-10.12_16465"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	4.49324373116e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
902	"Qld_RE_DomE_12.9-10.12_16505"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.12/12.9-10.2"	"90/10"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"90/10"	"9a"	"9"	"3"	8.68459217882e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
903	"Qld_RE_DomE_12.9-10.12_16507"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.28	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
904	"Qld_RE_DomE_12.9-10.12_16513"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
905	"Qld_RE_DomE_12.9-10.12_16517"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	5.98220731349e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
906	"Qld_RE_DomE_12.9-10.12_16530"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
912	"Qld_RE_DomE_12.9-10.12_16570"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.55534860893e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
913	"Qld_RE_DomE_12.9-10.12_16571"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	8.00746665839e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
914	"Qld_RE_DomE_12.9-10.12_16574"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
915	"Qld_RE_DomE_12.9-10.12_16581"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.74944700964e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
921	"Qld_RE_DomE_12.9-10.12_16608"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
922	"Qld_RE_DomE_12.9-10.12_16611"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.04	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
923	"Qld_RE_DomE_12.9-10.12_16620"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
924	"Qld_RE_DomE_12.9-10.12_16642"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
925	"Qld_RE_DomE_12.9-10.12_16657"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.77508026797e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
926	"Qld_RE_DomE_12.9-10.12_16658"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
927	"Qld_RE_DomE_12.9-10.12_16662"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
928	"Qld_RE_DomE_12.9-10.12_16672"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.68518564079e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
929	"Qld_RE_DomE_12.9-10.12_16687"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.15	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
930	"Qld_RE_DomE_12.9-10.12_16693"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.76239316052e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
931	"Qld_RE_DomE_12.9-10.12_16704"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
932	"Qld_RE_DomE_12.9-10.12_16718"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.45213979634e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
933	"Qld_RE_DomE_12.9-10.12_16722"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.20143282406e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
934	"Qld_RE_DomE_12.9-10.12_16727"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
935	"Qld_RE_DomE_12.9-10.12_16741"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	9.70106688921e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
936	"Qld_RE_DomE_12.9-10.12_16776"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
941	"Qld_RE_DomE_12.9-10.12_16911"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.19"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
942	"Qld_RE_DomE_12.9-10.12_16915"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.86108099359e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
943	"Qld_RE_DomE_12.9-10.12_16917"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"C"	"9a"	"100"	"9a"	"9"	"3"	5.82032193927e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
944	"Qld_RE_DomE_12.9-10.12_16926"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.0440140336e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
950	"Qld_RE_DomE_12.9-10.12_16974"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
956	"Qld_RE_DomE_12.9-10.12_17002"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.98120058312e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
957	"Qld_RE_DomE_12.9-10.12_17010"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.89093718308e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
958	"Qld_RE_DomE_12.9-10.12_17019"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.05	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
959	"Qld_RE_DomE_12.9-10.12_17020"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.0602382156e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
960	"Qld_RE_DomE_12.9-10.12_17028"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.13312661802e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
961	"Qld_RE_DomE_12.9-10.12_17029"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.44569316387e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
962	"Qld_RE_DomE_12.9-10.12_17033"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.04	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
963	"Qld_RE_DomE_12.9-10.12_17043"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
964	"Qld_RE_DomE_12.9-10.12_17046"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
965	"Qld_RE_DomE_12.9-10.12_17078"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.08439250388e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
966	"Qld_RE_DomE_12.9-10.12_17091"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
967	"Qld_RE_DomE_12.9-10.12_17098"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.8073301529e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
968	"Qld_RE_DomE_12.9-10.12_17100"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
969	"Qld_RE_DomE_12.9-10.12_17104"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.27766023495e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
970	"Qld_RE_DomE_12.9-10.12_17107"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.19"	"60/40"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"60/40"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
971	"Qld_RE_DomE_12.9-10.12_17108"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.19"	"60/40"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"60/40"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
972	"Qld_RE_DomE_12.9-10.12_17113"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
973	"Qld_RE_DomE_12.9-10.12_17123"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.13109320501e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
979	"Qld_RE_DomE_12.9-10.12_17146"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.74176998778e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
985	"Qld_RE_DomE_12.9-10.12_17166"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.64316453586e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
986	"Qld_RE_DomE_12.9-10.12_17179"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.56420911293e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
987	"Qld_RE_DomE_12.9-10.12_17181"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.30823106055e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
988	"Qld_RE_DomE_12.9-10.12_17183"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.89109400112e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
989	"Qld_RE_DomE_12.9-10.12_17184"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.13986339511e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
990	"Qld_RE_DomE_12.9-10.12_17187"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.10653559005e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
991	"Qld_RE_DomE_12.9-10.12_17189"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.73072336719e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
992	"Qld_RE_DomE_12.9-10.12_17190"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
993	"Qld_RE_DomE_12.9-10.12_17192"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.69700599468e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
994	"Qld_RE_DomE_12.9-10.12_17221"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
995	"Qld_RE_DomE_12.9-10.12_17222"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.39599178688e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
996	"Qld_RE_DomE_12.9-10.12_17226"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
997	"Qld_RE_DomE_12.9-10.12_17228"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.31592389829e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
998	"Qld_RE_DomE_12.9-10.12_17232"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.05033941795e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1004	"Qld_RE_DomE_12.9-10.12_17251"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.32081643996e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1005	"Qld_RE_DomE_12.9-10.12_17270"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	9.39574429457e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1011	"Qld_RE_DomE_12.9-10.12_17301"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.7"	"60/40"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"60/40"	"9a"	"9"	"3"	0.03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1048	"Qld_RE_DomE_12.9-10.12_17474"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	7.18162627714e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1049	"Qld_RE_DomE_12.9-10.12_17478"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	0.04	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1050	"Qld_RE_DomE_12.9-10.12_17491"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	4.93583200094e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1051	"Qld_RE_DomE_12.9-10.12_17494"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.44867470221e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1257	"Qld_RE_DomE_12.9-10.16_19614"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1258	"Qld_RE_DomE_12.9-10.16_19639"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1259	"Qld_RE_DomE_12.9-10.16_19642"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1260	"Qld_RE_DomE_12.9-10.16_19671"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	6.37559243354e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1261	"Qld_RE_DomE_12.9-10.6_16305"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"25a"	"100"	"25a"	"25"	"10"	0.01	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1012	"Qld_RE_DomE_12.9-10.12_17302"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.7"	"60/40"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"60/40"	"9a"	"9"	"3"	9.42269303963e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1013	"Qld_RE_DomE_12.9-10.12_17303"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.7"	"60/40"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"60/40"	"9a"	"9"	"3"	5.41279766171e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1014	"Qld_RE_DomE_12.9-10.12_17304"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	5.20837319658e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1015	"Qld_RE_DomE_12.9-10.12_17308"	"12.9-10.12/12.9-10.7a/12.9-10.2"	"12.9-10.12"	"12.9-10.7a"	"12.9-10.2"	" "	" "	"50/30/20"	50	30	20	0	0	"12.9-10.12/12.9-10.7/12.9-10.2"	"50/30/20"	"9-10"	"E/OC/NC"	254	"E/O/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/12a/10b"	"50/30/20"	"9a"	"9"	"3"	3.40748727056e-03	"RE_12.9-10.12/12.9-10.7a/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1016	"Qld_RE_DomE_12.9-10.12_17310"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1017	"Qld_RE_DomE_12.9-10.12_17316"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.7"	"60/40"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"60/40"	"9a"	"9"	"3"	0.15	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1018	"Qld_RE_DomE_12.9-10.12_17317"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9a"	"100"	"9a"	"9"	"3"	5.36159588561e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1019	"Qld_RE_DomE_12.9-10.12_17318"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.48892113544e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1020	"Qld_RE_DomE_12.9-10.12_17324"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	7.35318497028e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1021	"Qld_RE_DomE_12.9-10.12_17329"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.43028416772e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1022	"Qld_RE_DomE_12.9-10.12_17339"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.15419441879e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1023	"Qld_RE_DomE_12.9-10.12_17344"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.16024175848e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1028	"Qld_RE_DomE_12.9-10.12_17386"	"12.9-10.12/12.9-10.7"	"12.9-10.12"	"12.9-10.7"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/13c"	"70/30"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12/12.9-10.7"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1029	"Qld_RE_DomE_12.9-10.12_17400"	"12.9-10.12/12.9-10.7"	"12.9-10.12"	"12.9-10.7"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/13c"	"70/30"	"9a"	"9"	"3"	5.29602026347e-03	"RE_12.9-10.12/12.9-10.7"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1030	"Qld_RE_DomE_12.9-10.12_17401"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.95308331953e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1031	"Qld_RE_DomE_12.9-10.12_17402"	"12.9-10.12/12.9-10.4"	"12.9-10.12"	"12.9-10.4"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.4"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.80265111897e-03	"RE_12.9-10.12/12.9-10.4"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1032	"Qld_RE_DomE_12.9-10.12_17412"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.7"	"60/40"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"60/40"	"9a"	"9"	"3"	2.60780052416e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1033	"Qld_RE_DomE_12.9-10.12_17414"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.6971534123e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1034	"Qld_RE_DomE_12.9-10.12_17417"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1035	"Qld_RE_DomE_12.9-10.12_17424"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	8.04547564698e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1036	"Qld_RE_DomE_12.9-10.12_17428"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	5.49975160873e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1037	"Qld_RE_DomE_12.9-10.12_17435"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1038	"Qld_RE_DomE_12.9-10.12_17436"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	2.19900975157e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1039	"Qld_RE_DomE_12.9-10.12_17440"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.202359046e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1040	"Qld_RE_DomE_12.9-10.12_17441"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1041	"Qld_RE_DomE_12.9-10.12_17442"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.2"	"60/40"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"60/40"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1042	"Qld_RE_DomE_12.9-10.12_17445"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1043	"Qld_RE_DomE_12.9-10.12_17453"	"12.9-10.12/12.9-10.7a"	"12.9-10.12"	"12.9-10.7a"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.7"	"70/30"	"9-10"	"E/OC"	254	"E/O"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/12a"	"70/30"	"9a"	"9"	"3"	6.85095706286e-03	"RE_12.9-10.12/12.9-10.7a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1044	"Qld_RE_DomE_12.9-10.12_17459"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1045	"Qld_RE_DomE_12.9-10.12_17462"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.17317917148e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1046	"Qld_RE_DomE_12.9-10.12_17463"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1047	"Qld_RE_DomE_12.9-10.12_17466"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1052	"Qld_RE_DomE_12.9-10.12_17496"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	3.9413266206e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1053	"Qld_RE_DomE_12.9-10.12_17498"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	5.05582722773e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1054	"Qld_RE_DomE_12.9-10.12_17500"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	7.89095525177e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1055	"Qld_RE_DomE_12.9-10.12_17502"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	7.66192900874e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1056	"Qld_RE_DomE_12.9-10.12_17506"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.19"	"60/40"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"60/40"	"9a"	"9"	"3"	5.97457275842e-03	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1057	"Qld_RE_DomE_12.9-10.12_17513"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1058	"Qld_RE_DomE_12.9-10.12_17514"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1059	"Qld_RE_DomE_12.9-10.12_17519"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.19"	"60/40"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"60/40"	"9a"	"9"	"3"	7.00172801618e-03	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1060	"Qld_RE_DomE_12.9-10.12_17520"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.12/12.9-10.2"	"70/30"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"70/30"	"9a"	"9"	"3"	8.81702832169e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1061	"Qld_RE_DomE_12.9-10.12_17525"	"12.9-10.12/12.9-10.19a"	"12.9-10.12"	"12.9-10.19a"	" "	" "	" "	"60/40"	60	40	0	0	0	"12.9-10.12/12.9-10.19"	"60/40"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"60/40"	"9a"	"9"	"3"	3.701034341e-03	"RE_12.9-10.12/12.9-10.19a"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1062	"Qld_RE_DomE_12.9-10.12_17528"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1063	"Qld_RE_DomE_12.9-10.12_17547"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	2.8238174904e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1064	"Qld_RE_DomE_12.9-10.12_17550"	"12.9-10.12/12.9-10.2"	"12.9-10.12"	"12.9-10.2"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.2"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a/10b"	"80/20"	"9a"	"9"	"3"	6.66191647177e-03	"RE_12.9-10.12/12.9-10.2"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1065	"Qld_RE_DomE_12.9-10.12_17572"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1066	"Qld_RE_DomE_12.9-10.12_17575"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1067	"Qld_RE_DomE_12.9-10.12_17593"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1068	"Qld_RE_DomE_12.9-10.12_17598"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.41333372267e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1079	"Qld_RE_DomE_12.9-10.12_17631"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.8462961713e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1080	"Qld_RE_DomE_12.9-10.12_17632"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.04	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1081	"Qld_RE_DomE_12.9-10.12_17633"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1082	"Qld_RE_DomE_12.9-10.12_17635"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.39207212397e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1083	"Qld_RE_DomE_12.9-10.12_17637"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.74325536755e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1094	"Qld_RE_DomE_12.9-10.12_17667"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.42394085075e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1095	"Qld_RE_DomE_12.9-10.12_17671"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1096	"Qld_RE_DomE_12.9-10.12_17672"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.67957991608e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1097	"Qld_RE_DomE_12.9-10.12_17673"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.22571377648e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1098	"Qld_RE_DomE_12.9-10.12_17674"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1099	"Qld_RE_DomE_12.9-10.12_17676"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.22303971857e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1100	"Qld_RE_DomE_12.9-10.12_17681"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.73836242793e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1101	"Qld_RE_DomE_12.9-10.12_17683"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.85059933347e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1102	"Qld_RE_DomE_12.9-10.12_17685"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1103	"Qld_RE_DomE_12.9-10.12_17686"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.86486254269e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1104	"Qld_RE_DomE_12.9-10.12_17689"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1105	"Qld_RE_DomE_12.9-10.12_17690"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.71871230712e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1106	"Qld_RE_DomE_12.9-10.12_17691"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.70854041262e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1107	"Qld_RE_DomE_12.9-10.12_17694"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.10418339985e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1108	"Qld_RE_DomE_12.9-10.12_17698"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.45475398797e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1114	"Qld_RE_DomE_12.9-10.12_17723"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.83196621477e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1115	"Qld_RE_DomE_12.9-10.12_17725"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.70115029863e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1116	"Qld_RE_DomE_12.9-10.12_17729"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.10149177837e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1117	"Qld_RE_DomE_12.9-10.12_17731"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.97977353003e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1118	"Qld_RE_DomE_12.9-10.12_17735"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.34264178077e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1119	"Qld_RE_DomE_12.9-10.12_17748"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.28805878963e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1120	"Qld_RE_DomE_12.9-10.12_17750"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.12317733512e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1121	"Qld_RE_DomE_12.9-10.12_17753"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1122	"Qld_RE_DomE_12.9-10.12_17755"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	5.59413821178e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1123	"Qld_RE_DomE_12.9-10.12_17756"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.44695128209e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1124	"Qld_RE_DomE_12.9-10.12_17762"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.14196513333e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1125	"Qld_RE_DomE_12.9-10.12_17763"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	4.1138193928e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1126	"Qld_RE_DomE_12.9-10.12_17768"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1127	"Qld_RE_DomE_12.9-10.12_17777"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	9.15083607944e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1128	"Qld_RE_DomE_12.9-10.12_17783"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.06603477496e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1129	"Qld_RE_DomE_12.9-10.12_17791"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	3.31175362195e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1130	"Qld_RE_DomE_12.9-10.12_17806"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"9a"	"100"	"9a"	"9"	"3"	2.89637424922e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1131	"Qld_RE_DomE_12.9-10.12_17814"	"12.9-10.12/12.9-10.4"	"12.9-10.12"	"12.9-10.4"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.4"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.02	"RE_12.9-10.12/12.9-10.4"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1132	"Qld_RE_DomE_12.9-10.12_17818"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"9a"	"100"	"9a"	"9"	"3"	3.38929320053e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1133	"Qld_RE_DomE_12.9-10.12_17877"	"12.9-10.12/12.9-10.4"	"12.9-10.12"	"12.9-10.4"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.4"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12/12.9-10.4"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1134	"Qld_RE_DomE_12.9-10.12_17938"	"12.9-10.12/12.9-10.4"	"12.9-10.12"	"12.9-10.4"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.4"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	7.12988628783e-03	"RE_12.9-10.12/12.9-10.4"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1135	"Qld_RE_DomE_12.9-10.12_18007"	"12.9-10.12/12.9-10.4"	"12.9-10.12"	"12.9-10.4"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.12/12.9-10.4"	"80/20"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	6.56243268656e-03	"RE_12.9-10.12/12.9-10.4"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1136	"Qld_RE_DomE_12.9-10.12_18051"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1137	"Qld_RE_DomE_12.9-10.12_18056"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1138	"Qld_RE_DomE_12.9-10.12_18057"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.04	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1139	"Qld_RE_DomE_12.9-10.12_18070"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9a"	"100"	"9a"	"9"	"3"	0.01	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1140	"Qld_RE_DomE_12.9-10.12_18078"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"9a"	"100"	"9a"	"9"	"3"	8.05734632807e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1141	"Qld_RE_DomE_12.9-10.12_18082"	"12.9-10.12"	"12.9-10.12"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.12"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"9a"	"100"	"9a"	"9"	"3"	5.83552466941e-03	"RE_12.9-10.12"	"12.9-10.12"	120912.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"No representation"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa +/- E. siderophloia, E. tereticornis, E. racemosa subsp. racemosa, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Does not include areas dominated by Eucalyptus racemosa subsp. racemosa. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)
 Vegetation communities in this regional ecosystem include: 
12.9-10.12a:  Eucalyptus interstans, Angophora leiocarpa +/- Corymbia intermedia, E. tereticornis C. tessellaris, E. siderophloia, C. citriodora subsp. variegata woodland to open forest. Lophostemon suaveolens is often present as a sub canopy or understorey tree. Occasional Melaleuca quinquenervia on lower slopes. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 9a)"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Eucalyptus seeana, Corymbia intermedia, Angophora leiocarpa woodland on sedimentary rocks"	"Bean et al. (1998), H36, H39j, H7"	"2, (3)"	"No representation"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"12.9-10.12: Occurs on south-west outskirts of Brisbane. Subject to increasing fragmentation and urbanisation. Eucalyptus seeana is often a subdominant component of this Regional ecosystem. Areas of this regional ecosystem on remnant Tertiary surfaces that are mappable (>2ha) are defined as 12.5.3a.
12.9-10.12a: Occurs near Esk. Subject to increasing fragmentation and urbanisation. Eucalyptus interstans is often a subdominant component of this Regional ecosystem."		12.00	9.00		"Sparse"	"W"	"9a"
1151	"Qld_RE_DomE_12.9-10.15_18061"	"12.9-10.15/12.9-10.17"	"12.9-10.15"	"12.9-10.17"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.9-10.15/12.9-10.17"	"95/5"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a/9a"	"95/5"	"7a"	"7"	"1"	0.01	"RE_12.9-10.15/12.9-10.17"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1152	"Qld_RE_DomE_12.9-10.15_18077"	"12.9-10.15/12.9-10.17"	"12.9-10.15"	"12.9-10.17"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.9-10.15/12.9-10.17"	"95/5"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a/9a"	"95/5"	"7a"	"7"	"1"	7.05766140493e-03	"RE_12.9-10.15/12.9-10.17"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1153	"Qld_RE_DomE_12.9-10.15_18083"	"12.9-10.15/12.9-10.17"	"12.9-10.15"	"12.9-10.17"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.9-10.15/12.9-10.17"	"95/5"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a/9a"	"95/5"	"7a"	"7"	"1"	0.01	"RE_12.9-10.15/12.9-10.17"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1154	"Qld_RE_DomE_12.9-10.15_18101"	"12.9-10.15/12.9-10.17"	"12.9-10.15"	"12.9-10.17"	" "	" "	" "	"95/5"	95	5	0	0	0	"12.9-10.15/12.9-10.17"	"95/5"	"9-10"	"E/NC"	254	"E/L"	67	"E-dom"	"8.0"	50	"A"	"A"	"7a/9a"	"95/5"	"7a"	"7"	"1"	9.76591617478e-03	"RE_12.9-10.15/12.9-10.17"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1159	"Qld_RE_DomE_12.9-10.15_18616"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"A"	"7a"	"100"	"7a"	"7"	"1"	5.51626105885e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1160	"Qld_RE_DomE_12.9-10.15_18619"	"12.9-10.15/12.9-10.16"	"12.9-10.15"	"12.9-10.16"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.15/12.9-10.16"	"80/20"	"9-10"	"E/E"	254	"E/O"	67	"E-dom"	"8.0"	50	"B"	"A"	"7a/5a"	"80/20"	"7a"	"7"	"1"	0.02	"RE_12.9-10.15/12.9-10.16"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1161	"Qld_RE_DomE_12.9-10.15_18664"	"12.9-10.15/12.9-10.16"	"12.9-10.15"	"12.9-10.16"	" "	" "	" "	"80/20"	80	20	0	0	0	"12.9-10.15/12.9-10.16"	"80/20"	"9-10"	"E/E"	254	"E/O"	67	"E-dom"	"8.0"	50	"B"	"A"	"7a/5a"	"80/20"	"7a"	"7"	"1"	4.90585854094e-03	"RE_12.9-10.15/12.9-10.16"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1162	"Qld_RE_DomE_12.9-10.15_18741"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"7a"	"100"	"7a"	"7"	"1"	8.21308973696e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1163	"Qld_RE_DomE_12.9-10.15_18764"	"12.9-10.15/12.9-10.16/12.9-10.6"	"12.9-10.15"	"12.9-10.16"	"12.9-10.6"	" "	" "	"40/30/30"	40	30	30	0	0	"12.9-10.15/12.9-10.16/12.9-10.6"	"40/30/30"	"9-10"	"E/E/E"	254	"E/O/E"	67	"E-dom"	"8.0"	50	"B"	"B"	"7a/5a/25a"	"40/30/30"	"7a"	"7"	"1"	0.01	"RE_12.9-10.15/12.9-10.16/12.9-10.6"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1164	"Qld_RE_DomE_12.9-10.15_18770"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"7a"	"100"	"7a"	"7"	"1"	9.72128784772e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1165	"Qld_RE_DomE_12.9-10.15_18790"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"7a"	"100"	"7a"	"7"	"1"	7.85436759963e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1166	"Qld_RE_DomE_12.9-10.15_18804"	"12.9-10.15"	"12.9-10.15"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.15"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"7a"	"100"	"7a"	"7"	"1"	6.13875863908e-03	"RE_12.9-10.15"	"12.9-10.15"	120915.00	"Endangered"	"Endangered"		"In September 2011, remnant extent was < 10,000 ha and 10-30% of the pre-clearing area remained"	"Low"	"Low microphyll vine forest +/- Araucaria cunninghamii and semi-evergreen vine thicket. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 7a)"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Semi-evergreen vine thicket with Brachychiton rupestris on sedimentary rocks"	"Bean et al. (1998), G18, H1"	"2, 5, (6), (1)"	"Conondale NP, Benarkin NP, Cressbrook CP, Main Range NP, Dwyers Scrub CP, Cherbourg CP, Tenthill CP, [Gatton NP]"	"Habitat for near threatened flora species including Callitris baileyi."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance."	"Characteristic localities for the RE are Lockyer and Fassifern Valleys. Extensively cleared for pasture and cropping. Remnants require intensive management because of invasion by weeds and fire damage on margins. In places the RE grades into RE 12.9-10.6."		12.00	9.00		"Dense"	"LCF"	"7a"
1171	"Qld_RE_DomE_12.9-10.16_17704"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1172	"Qld_RE_DomE_12.9-10.16_17714"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	9.17721169596e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1173	"Qld_RE_DomE_12.9-10.16_17717"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	8.77850734641e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1174	"Qld_RE_DomE_12.9-10.16_17718"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	3.41885878939e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1175	"Qld_RE_DomE_12.9-10.16_17726"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	5.95007429734e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1176	"Qld_RE_DomE_12.9-10.16_17782"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1177	"Qld_RE_DomE_12.9-10.16_17788"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	2.93529799153e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1178	"Qld_RE_DomE_12.9-10.16_17796"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	3.91113823138e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1179	"Qld_RE_DomE_12.9-10.16_17802"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	8.42999958655e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1180	"Qld_RE_DomE_12.9-10.16_17805"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.07	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1181	"Qld_RE_DomE_12.9-10.16_17825"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	5.67985942164e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1182	"Qld_RE_DomE_12.9-10.16_17833"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.04	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1183	"Qld_RE_DomE_12.9-10.16_17867"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1184	"Qld_RE_DomE_12.9-10.16_17884"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1185	"Qld_RE_DomE_12.9-10.16_17893"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1186	"Qld_RE_DomE_12.9-10.16_18014"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1187	"Qld_RE_DomE_12.9-10.16_18037"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	3.99383829776e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1188	"Qld_RE_DomE_12.9-10.16_18136"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	7.94924719722e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1189	"Qld_RE_DomE_12.9-10.16_18629"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1190	"Qld_RE_DomE_12.9-10.16_18649"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1191	"Qld_RE_DomE_12.9-10.16_18675"	"12.9-10.16/12.9-10.17"	"12.9-10.16"	"12.9-10.17"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.16/12.9-10.17"	"70/30"	"9-10"	"E/NC"	254	"O/L"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a/9a"	"70/30"	"5a"	"5"	"1"	0.03	"RE_12.9-10.16/12.9-10.17"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1192	"Qld_RE_DomE_12.9-10.16_18692"	"12.9-10.16/12.9-10.17"	"12.9-10.16"	"12.9-10.17"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.16/12.9-10.17"	"70/30"	"9-10"	"E/NC"	254	"O/L"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a/9a"	"70/30"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16/12.9-10.17"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1193	"Qld_RE_DomE_12.9-10.16_18802"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1194	"Qld_RE_DomE_12.9-10.16_18848"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"A"	"5a"	"100"	"5a"	"5"	"1"	7.08681606301e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1205	"Qld_RE_DomE_12.9-10.16_19214"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	5.80140262092e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1206	"Qld_RE_DomE_12.9-10.16_19233"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1207	"Qld_RE_DomE_12.9-10.16_19242"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1208	"Qld_RE_DomE_12.9-10.16_19251"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1209	"Qld_RE_DomE_12.9-10.16_19253"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1215	"Qld_RE_DomE_12.9-10.16_19280"	"12.9-10.16/12.9-10.3"	"12.9-10.16"	"12.9-10.3"	" "	" "	" "	"90/10"	90	10	0	0	0	"12.9-10.16/12.9-10.3"	"90/10"	"9-10"	"E/OC"	254	"O/O"	117	"O-dom"	"8.0"	50	"B"	"C"	"5a/13d"	"90/10"	"5a"	"5"	"1"	8.39574735152e-03	"RE_12.9-10.16/12.9-10.3"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1216	"Qld_RE_DomE_12.9-10.16_19315"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	9.48704931065e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1217	"Qld_RE_DomE_12.9-10.16_19323"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	3.90279492638e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1218	"Qld_RE_DomE_12.9-10.16_19324"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1223	"Qld_RE_DomE_12.9-10.16_19381"	"12.9-10.16/12.8.4"	"12.9-10.16"	"12.8.4"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.16/12.8.4"	"70/30"	"9-10"	"E/NC"	254	"O/L"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a/2a"	"70/30"	"5a"	"5"	"1"	8.49158930615e-03	"RE_12.9-10.16/12.8.4"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1224	"Qld_RE_DomE_12.9-10.16_19388"	"12.9-10.16/12.8.4"	"12.9-10.16"	"12.8.4"	" "	" "	" "	"70/30"	70	30	0	0	0	"12.9-10.16/12.8.4"	"70/30"	"9-10"	"E/NC"	254	"O/L"	117	"O-dom"	"8.0"	50	"B"	"B"	"5a/2a"	"70/30"	"5a"	"5"	"1"	7.26501813745e-03	"RE_12.9-10.16/12.8.4"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1225	"Qld_RE_DomE_12.9-10.16_19399"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1226	"Qld_RE_DomE_12.9-10.16_19427"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1232	"Qld_RE_DomE_12.9-10.16_19476"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	7.6119015757e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1233	"Qld_RE_DomE_12.9-10.16_19482"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	6.62278787371e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1234	"Qld_RE_DomE_12.9-10.16_19483"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1235	"Qld_RE_DomE_12.9-10.16_19484"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1236	"Qld_RE_DomE_12.9-10.16_19499"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	8.73959986293e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1237	"Qld_RE_DomE_12.9-10.16_19500"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1238	"Qld_RE_DomE_12.9-10.16_19502"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	9.60587501327e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1239	"Qld_RE_DomE_12.9-10.16_19505"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	7.42944973124e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1240	"Qld_RE_DomE_12.9-10.16_19508"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1241	"Qld_RE_DomE_12.9-10.16_19511"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	8.9164007374e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1247	"Qld_RE_DomE_12.9-10.16_19534"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1248	"Qld_RE_DomE_12.9-10.16_19545"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1249	"Qld_RE_DomE_12.9-10.16_19553"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1250	"Qld_RE_DomE_12.9-10.16_19560"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	5.49143732254e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1251	"Qld_RE_DomE_12.9-10.16_19565"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	4.39101835813e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1252	"Qld_RE_DomE_12.9-10.16_19571"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.01	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1253	"Qld_RE_DomE_12.9-10.16_19577"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	5.64548499558e-03	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1254	"Qld_RE_DomE_12.9-10.16_19584"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"B"	"5a"	"100"	"5a"	"5"	"1"	0.02	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1255	"Qld_RE_DomE_12.9-10.16_19600"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.07	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1256	"Qld_RE_DomE_12.9-10.16_19602"	"12.9-10.16"	"12.9-10.16"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.16"	"100"	"9-10"	"E"	254	"O"	117	"O-dom"	"8.0"	50	"A"	"A"	"5a"	"100"	"5a"	"5"	"1"	0.17	"RE_12.9-10.16"	"12.9-10.16"	120916.00	"Of concern"	"Endangered"	"Under review"	"In September 2011, remnant extent was < 10,000 ha and >30% of the pre-clearing area remained"	"High"	"Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Argyrodendron sp.(Kin Kin W.D.Francis AQ81198), Araucaria cunninghamii, Agathis robusta, Backhousia myrtifolia, Cupaniopsis parvifolia, Dendrocnide photinophylla, Rhodosphaera rhodanthema, Flindersia australis, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 5a)"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Araucarian microphyll to notophyll vine forest on Cainozoic and Mesozoic sediments"	"Bean et al. (1998), G10, G11 (in part), G9"	"2, 7, 6, 4, 1, 8, 5, 9"	"Wongi NP, Glenbar NP, Mount Barney NP, Fairlies Knob NP, Lamington NP, Mount Bauple NP (S), Dularcha NP, Mount Chinghee NP, Glass House Mountains NP, Mount Binga NP, Tarong NP, Great Sandy NP, Noosa NP, Tewantin NP, Nangur NP, The Palms NP, Main Range NP, Crohamhurst CP, [King CP], [Eudlo Creek CP], [Bullyard CP]"	"Habitat for threatened flora species including Alectryon ramiflorus, Corchorus cunninghamii, Planchonella eerwah, Plectranthus omissus, Sarcochilus weinthalii, Cupaniopsis shirleyana, C. tomentella and near threatened species including Hernandia bivalvis."	"STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. Some preliminary work suggests rainforest seedling germination from planned burning activities will assist the establishment of seedlings in newly burnt areas, especially due to smoke. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research."	"Characteristic localities for the RE are Seaview Range near Brooweena, Tinana Creek and Flinders Peak area. Extensively cleared for pasture and cropping. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. Agathis robusta has a restricted distribution in the bioregion."		12.00	9.00		"Dense"	"CF"	"5a"
1262	"Qld_RE_DomE_12.9-10.6_16317"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"25a"	"100"	"25a"	"25"	"10"	5.82751033262e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1263	"Qld_RE_DomE_12.9-10.6_16333"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"25a"	"100"	"25a"	"25"	"10"	5.55903038069e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1264	"Qld_RE_DomE_12.9-10.6_16403"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"25a"	"100"	"25a"	"25"	"10"	4.84717387025e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1265	"Qld_RE_DomE_12.9-10.6_16458"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"25a"	"100"	"25a"	"25"	"10"	5.61691454567e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1266	"Qld_RE_DomE_12.9-10.6_16468"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"B"	"B"	"25a"	"100"	"25a"	"25"	"10"	2.27623459565e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1267	"Qld_RE_DomE_12.9-10.6_18019"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.51215594876e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1268	"Qld_RE_DomE_12.9-10.6_18022"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	5.43136968374e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1269	"Qld_RE_DomE_12.9-10.6_18026"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	5.76531864334e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1270	"Qld_RE_DomE_12.9-10.6_18038"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	5.56334690417e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1271	"Qld_RE_DomE_12.9-10.6_18044"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	4.6361193336e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1272	"Qld_RE_DomE_12.9-10.6_18048"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	6.93370011187e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1273	"Qld_RE_DomE_12.9-10.6_18060"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	0.01	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1274	"Qld_RE_DomE_12.9-10.6_18063"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	8.51591985817e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1275	"Qld_RE_DomE_12.9-10.6_18105"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	3.57472948134e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1276	"Qld_RE_DomE_12.9-10.6_18109"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	4.38103527192e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1277	"Qld_RE_DomE_12.9-10.6_18201"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	8.05398555184e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1278	"Qld_RE_DomE_12.9-10.6_18203"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	4.39858821512e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1279	"Qld_RE_DomE_12.9-10.6_18217"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	9.93191391667e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1280	"Qld_RE_DomE_12.9-10.6_18220"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	8.01536770497e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1281	"Qld_RE_DomE_12.9-10.6_18223"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	5.76332952916e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1292	"Qld_RE_DomE_12.9-10.6_18369"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.05835912706e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1293	"Qld_RE_DomE_12.9-10.6_18390"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.51993546376e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1294	"Qld_RE_DomE_12.9-10.6_18413"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	7.51387846063e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1295	"Qld_RE_DomE_12.9-10.6_18427"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	8.10888997858e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1296	"Qld_RE_DomE_12.9-10.6_18435"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	4.76501586708e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1297	"Qld_RE_DomE_12.9-10.6_18450"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	5.19296350283e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1298	"Qld_RE_DomE_12.9-10.6_18455"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	4.46734743358e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1299	"Qld_RE_DomE_12.9-10.6_18484"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	6.69593497406e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1300	"Qld_RE_DomE_12.9-10.6_18487"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	9.86812766175e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1301	"Qld_RE_DomE_12.9-10.6_18506"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	0.01	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1302	"Qld_RE_DomE_12.9-10.6_18599"	"12.9-10.6"	"12.9-10.6"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.6"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"A"	"25a"	"100"	"25a"	"25"	"10"	4.0006803566e-03	"RE_12.9-10.6"	"12.9-10.6"	120906.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"No representation"	"Acacia harpophylla open forest +/- Casuarina cristata and vine thicket species. Occurs on Cainozoic and Mesozoic sediments, especially fine-grained rocks. (BVG1M: 25a)"	"Acacia harpophylla open forest on sedimentary rocks"	"Acacia harpophylla open forest on sedimentary rocks"	"Bean et al. (1998), H47"	"2, (5)"	"No representation"		"STRATEGY: Planned burns should be used to protect scrubs at their margins from fire incursion and to reduce fuel loads in order to prevent the spread of wildfire. Burn less than 10% in any year. Small and spaced spot fires lit on the edge of remnants should be used to draw fire away from the perimeter of remnants using prevailing wind conditions. ISSUES: This vegetation primarily requires protection from fire, however carefully managed low intensity fires will be useful in buffering remnants from surrounding vegetation and reducing fuel loads, leading to overall protection of the RE from wildfire. Moderate fires may assist in the regeneration of hard-seeded species and occasional high intensity fires may enhance acacia regeneration. Frequent fires may eliminate acacia, casuarina and other obligate seeding species. Remnants can be degraded by wildfire and planned burns if implemented inappropriately."	"Characteristic localities for the RE are the Lockyer Valley and west of Boonah. Extensively cleared for pasture and cropping. Only very small areas remain and these are subject to weed invasion, e.g. Asparagus Africans."		12.00	9.00		"Mid-dense"	"OF"	"25a"
1303	"Qld_RE_DomE_12.9-10.8_17860"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"C"	"A"	"17b"	"100"	"17b"	"17"	"5"	6.14982374482e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1304	"Qld_RE_DomE_12.9-10.8_17940"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"C"	"A"	"17b"	"100"	"17b"	"17"	"5"	6.5863371851e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1305	"Qld_RE_DomE_12.9-10.8_18236"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	3.00440430194e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1306	"Qld_RE_DomE_12.9-10.8_18266"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	1.67373401618e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1307	"Qld_RE_DomE_12.9-10.8_18282"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	8.71445649871e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1308	"Qld_RE_DomE_12.9-10.8_18294"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	0.01	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1309	"Qld_RE_DomE_12.9-10.8_18308"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	2.48761485345e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1310	"Qld_RE_DomE_12.9-10.8_18311"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	0.01	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1311	"Qld_RE_DomE_12.9-10.8_18312"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	4.29770927869e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1312	"Qld_RE_DomE_12.9-10.8_18318"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	9.99587242384e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
1313	"Qld_RE_DomE_12.9-10.8_18332"	"12.9-10.8"	"12.9-10.8"	" "	" "	" "	" "	"100"	100	0	0	0	0	"12.9-10.8"	"100"	"9-10"	"E"	254	"E"	67	"E-dom"	"8.0"	50	"A"	"B"	"17b"	"100"	"17b"	"17"	"5"	3.71661324198e-03	"RE_12.9-10.8"	"12.9-10.8"	120908.00	"Endangered"	"Endangered"		"In September 2011, <10% of the pre-clearing area remained."	"Low"	"Eucalyptus melanophloia grassy woodland, usually with E. crebra, Eucalyptus tereticornis +/- Corymbia tessellaris, C. erythrophloia and Angophora spp. Occurs on Cainozoic and Mesozoic sediments. (BVG1M: 17b)"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Eucalyptus melanophloia, E. crebra woodland on sedimentary rocks"	"Bean et al. (1998), I11"	"5, 2, 6, (10), (7)"	"Glenbar NP, Benarkin NP"		"SEASON: Summer to winter. INTENSITY: Low to moderate. INTERVAL: 4-25 years. STRATEGY: Aim for 40-60% mosaic burn. Burn with soil moisture and with a spot ignition strategy so that a patchwork of burnt/unburnt country is achieved. ISSUES: The fire regime should maintain a mosaic of grassy and shrubby understoreys. Control of weeds is a major focus of planned burning in most areas. Careful thought should be given to maintaining ground litter and fallen timber habitats by burning only with sufficient soil moisture. Burning should aim to produce fine scale mosaics of unburnt areas. Variability in season and fire intensity is important, as well as spot ignition in cooler or moister periods to encourage mosaics."	"Extensively cleared for pasture. This RE has a very patchy distribution and often occurs as patches too small to map at 1:100 000 scale."		12.00	9.00		"Sparse"	"W"	"17b"
