Threatened flora species habitat
Key Finding
Threatened flora habitat loss is ongoing in Queensland.
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Queensland or bioregion:
Bioregion (select locations to filter information)
Queensland
Pre-clearing habitat extent for 700 of Queensland’s endangered and vulnerable flora species was modelled and mapped for Queensland. Prior to land clearing, habitat was widespread in Queensland for:
- 194 threatened eucalypt forest and woodland species
- 335 threatened rainforest and scrub species
- 25 threatened Acacia forest, woodland and shrubland species
- 50 threatened wetland and Melaleuca open woodland species
- 17 threatened grassland and forbland species
- 79 threatened heath and other coastal community species.
Prior to land clearing, the largest extent of threatened flora habitat was found in the Brigalow Belt bioregion, with the exception of habitat for threatened heath and other coastal community species, which was most extensive in South East Queensland. Pre-clearing habitat for threatened eucalypt forest and woodland species, rainforest and scrub species as well as grassland and forbland species was also extensive in the South East Queensland bioregion. Large areas of pre-clearing habitat for threatened Acacia forest, woodland and shrubland species and wetland and Melaleuca open woodland species was found in the Mulga Lands and Mitchell Grass Downs bioregions.
Although most habitat loss for Queensland’s threatened flora occurred before 1997, habitat for threatened flora continues to be cleared. While additional remnant habitat for threatened heath and other coastal flora species in South East Queensland (see detail for SEQ) was mapped in 2013, clearing of this habitat is ongoing.
- 32% to 40% of pre-clearing habitat for most threatened flora groups had been cleared 2017.
- Threatened grassland and forbland flora is the exception, with 60% of habitat cleared prior to 2017.
Land clearing in Queensland between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Brigalow Belt
Pre-clearing habitat extent for 215 currently threatened flora species was modelled for the Brigalow Belt (BRB) bioregion. Prior to land clearing, BRB provided habitat for:
- 111 threatened eucalypt forest and woodland species
- 47 threatened rainforest and scrub species
- 15 threatened Acacia forest, woodland and shrubland species
- 13 threatened wetland and Melaleuca open woodland species
- 10 threatened grassland and forbland species
- 19 threatened heath and other coastal community species.
BRB experienced ongoing loss of habitat for all threatened flora groups between 1997 and 2017.
This list shows the percentage of pre-cleared habitat for threatened species that had been cleared by 2017 in BRB:
- 48% threatened eucalypt forest and woodland species
- 63% threatened rainforest and scrub flora
- 77% threatened Acacia forest, woodland and shrubland flora
- 65% threatened wetland and Melaleuca open woodland species
- 64% threatened grassland and forbland flora
- 27% threatened heath and other coastal community flora
BRB land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Cape York Peninsula
Pre-clearing habitat extent for 144 currently threatened flora species was modelled for the Cape York Peninsular (CYP) bioregion. Prior to land clearing, CYP provided habitat for:
- 17 threatened eucalypt forest and woodland species
- 100 threatened rainforest and scrub species
- 19 threatened wetland and Melaleuca open woodland species
- 1 threatened grassland and forbland species
- 6 threatened heath and other coastal community species.
CYP experienced ongoing loss of habitat between 1997 and 2017 for most threatened flora groups.
- There has been no clearing of threatened grassland and forbland species and threatened heath and other coastal species habitat since 1997.
- 99% of pre-clearing habitat for threatened eucalypt forest and woodland flora remained in 2017.
- 98% of pre-clearing habitat for threatened rainforest and scrub flora remains uncleared.
- Over 99% of pre-clearing habitat for threatened wetland and Melaleuca open woodland flora remained uncleared in 2017.
- 81% of pre-clearing habitat for threatened grassland and forbland species remained in 1997.
- Over 99% of the pre-clearing habitat for threatened heath and other coastal community flora remains uncleared in 2017.
CYP land clearing between 1997 and 2017 was primarily for mining and pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Central Queensland Coast
Pre-clearing habitat extent for 71 currently threatened flora species was modelled for Central Queensland Coast (CQC) bioregion. Prior to land clearing, CQC provided habitat for:
- 26 threatened eucalypt forest and woodland species
- 34 threatened rainforest and scrub species
- 1 threatened Acacia forest, woodland and shrubland species
- 3 threatened wetland and Melaleuca open woodland species
- 2 threatened grassland and forbland species
- 4 threatened heath and other coastal community species.
CQC experienced ongoing habitat loss between 1997 and 2017 in all but 2 flora groups.
- Habitat for threatened Acacia forest, woodland and shrubland species and grassland and forbland species have both remained largely uncleared since 1997.
- 87% of pre-clearing habitat for threatened eucalypt forest and woodland flora remained in 2017.
- 71% of pre-clearing habitat for threatened rainforest and scrub flora habitat was uncleared in 2017.
- 88% of pre-clearing habitat for threatened Acacia forest, woodland and shrubland flora was remnant in 1997 with no further habitat loss recorded to 2017.
- 76% of pre-clearing threatened wetland and Melaleuca open woodland flora remained in 2017.
- 17% of the pre-clearing habitat for threatened grassland and forbland flora had been cleared by 1997 but no further habitat loss has occurred to 2017.
- 98% of pre-clearing habitat for heath and other coastal community flora remained in 2017.
CQC land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Channel Country
Pre-clearing habitat extent for 17 currently threatened flora species was modelled for the Channel Country (CHC) bioregion. Prior to land clearing, CHC provided habitat for:
- 1 threatened eucalypt forest and woodland species
- 8 threatened Acacia forest, woodland and shrubland species
- 4 threatened wetland and Melaleuca open woodland species
- 3 threatened grassland and forbland species.
CHC experienced ongoing habitat loss between 1997 and 2017 for threatened Acacia forest, woodland and shrubland species and wetland and Melaleuca open woodlands species. No habitat has been cleared for threatened eucalypt forest and woodland species or threatened grassland and forbland species since 1997.
- Less than 1% of habitat for all threatened flora groups in the CHC bioregion had cleared by 2017.
CHC land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Desert Uplands
Pre-clearing habitat extent for 49 currently threatened flora species was modelled for the Desert Uplands (DEU) bioregion. Prior to land clearing, DEU provided habitat for:
- 14 threatened eucalypt forest and woodland species
- 4 threatened rainforest and scrub species
- 9 threatened Acacia forest, woodland and shrubland species
- 14 threatened wetland and Melaleuca open woodland species
- 5 threatened grassland and forbland species
- 2 threatened heath and other coastal community species.
DEU experienced ongoing habitat loss between 1997 and 2017 for all but 2 flora groups, threatened grassland and forbland species and heath and other coastal community species.
- Between 77% and 100% of pre-clearing habitat for all DEU threatened flora groups remained uncleared by 2017.
- Habitat for threatened heath and other coastal community flora has remained uncleared since 1997.
- Habitat for threatened grassland and forbland flora has remained uncleared since 2003.
DEU land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Einasleigh Uplands
Pre-clearing habitat extent for 99 currently threatened flora species was modelled for the Einasleigh Uplands (EIU) bioregion. Prior to land clearing, EIU provided habitat for:
- 36 threatened eucalypt forest and woodland species
- 37 threatened rainforest and scrub species
- 5 threatened Acacia forest, woodland and shrubland species
- 11 threatened wetland and Melaleuca open woodland species
- 1 threatened grassland and forbland species
- 8 threatened heath and other coastal community species.
EIU experienced ongoing habitat loss since 1997 for all threatened flora groups.
- At least 94% of pre-clearing habitat for all threatened flora groups remained uncleared by 2017.
EIU land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Gulf Plains
Pre-clearing habitat extent for 35 currently threatened flora species was modelled for the Gulf Plains (GUP) bioregion. Prior to land clearing, GUP provided habitat for:
- 13 threatened eucalypt forest and woodland species
- 9 threatened rainforest and scrub species
- 4 threatened Acacia forest, woodland and shrubland species
- 6 threatened wetland and Melaleuca open woodland species
- 2 threatened grassland and forbland species.
GUP experienced ongoing loss of habitat for all threatened flora groups between 1997 and 2017 with the exception of threatened grassland and forbland species which has remained uncleared since 2005.
- 96%–100% of pre-clearing habitat for all threatened flora groups remained uncleared in GUP in 2017.
GUP land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Mitchell Grass Downs
Pre-clearing habitat extent for 44 currently threatened flora species was modelled for the Mitchell Grass Downs (MGD) bioregion. Prior to land clearing, MGD provided habitat for:
- 9 threatened eucalypt forest and woodland species
- 2 threatened rainforest and scrub species
- 11 threatened Acacia forest, woodland and shrubland species
- 13 threatened wetland and Melaleuca open woodland species
- 8 threatened grassland and forbland species.
MGD experienced ongoing loss of habitat between 1997 and 2017 for all threatened flora groups.
- At least 86% of pre-clearing habitat remained uncleared by 2017 for most threatened flora groups with the exception of rainforest and scrub species where 60% of habitat had been cleared by 2017.
MGD land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Mulga Lands
Pre-clearing habitat extent for 32 currently threatened flora species was modelled for the Mulga Lands (MUL) bioregion. Prior to land clearing, MUL provided habitat for:
- 9 threatened eucalypt forest and woodland species
- 1 threatened rainforest and scrub species
- 9 threatened Acacia forest, woodland and shrubland species
- 7 threatened wetland and Melaleuca open woodland species
- 4 threatened grassland and forbland species
- 1 threatened heath and other coastal community species.
MUL experienced ongoing habitat loss between 1997 and 2017 for all but 1 flora group, threatened heath and other coastal community species.
- 92% of habitat for threatened wetlands and Melaleuca open woodland flora and 90% of habitat for threatened Acacia forest, woodland and shrubland flora remained uncleared in 2017.
- 63% of the pre-clearing habitat for threatened eucalypt forest and woodland flora and 52% of threatened grassland and forbland flora was remnant vegetation in 2017.
- Only 23% of pre-clearing habitat for threatened rainforest and scrub species remained in 2017.
- Only 3% of pre-clearing habitat for threatened heath and other coastal community flora remained uncleared in 2017.
MUL land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
New England Tableland
Pre-clearing habitat extent for 77 currently threatened flora species was modelled for the New England Tablelands (NET) bioregion. Prior to land clearing, NET provided habitat for:
- 40 threatened eucalypt forest and woodland species
- 12 threatened rainforest and scrub species
- 3 threatened Acacia forest, woodland and shrubland species
- 2 threatened wetland and Melaleuca open woodland species
- 6 threatened grassland and forbland species
- 13 threatened heath and other coastal community species.
NET experienced ongoing habitat loss for all threatened flora groups between 1997 and 2017.
- By 2017, only threatened heath and other coastal community flora retained more than half (51%) of its pre-clearing habitat extent.
- More than half of the pre-clearing habitat for threatened eucalypt forest and woodland flora (63%), rainforest and scrub flora (61%), wetland and Melaleuca open woodland flora (55%) and grassland and forbland flora (63%) had been cleared prior to 2017.
- Less than one-third (28%) of habitat for threatened Acacia forest, woodland and shrubland flora remained uncleared by 2017.
NET land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Northwest Highlands
Pre-clearing habitat extent for 5 currently threatened flora species was modelled for the Northwest Highlands (NWH) bioregion. Prior to land clearing, NWH provided habitat for:
- 3 threatened eucalypt forest and woodland species
- 2 threatened Acacia forest, woodland and shrubland species.
The loss of threatened eucalypt forest and woodland flora habitat is ongoing in the NWH bioregion. No habitat for threatened Acacia forest, woodland and shrubland flora has been cleared since 2005.
- More than 99% of pre-clear habitat for threatened eucalypt forest and woodland flora and threatened Acacia forest, woodland and shrubland flora remained in 2017.
NWH land clearing between 1997 and 2017 was primarily for pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Southeast Queensland
Pre-clearing habitat extent for 244 currently threatened flora species was modelled for the South East Queensland (SEQ) bioregion. Prior to land clearing, SEQ provided habitat for:
- 79 threatened eucalypt forest and woodland species
- 101 threatened rainforest and scrub species
- 5 threatened Acacia forest, woodland and shrubland species
- 12 threatened wetland and Melaleuca open woodland species
- 6 threatened grassland and forbland species
- 40 threatened heath and other coastal community species.
SEQ experienced ongoing habitat loss for all threatened flora groups between 1997 and 2017. Remapping to 1:25,000 scale using Lidar tree height data for 2 SEQ local government areas has detected the recovery of 9,405 hectares of previously disturbed vegetation to remnant status in the period to 2015.
- 85% of pre-clearing habitat for threatened Acacia forest, woodland and shrubland flora was cleared by 2017.
- 65% of pre-clearing habitat for threatened grassland and forbland flora was cleared by 2017.
- 55% of pre-clearing habitat for threatened eucalypt forest and woodland flora was cleared by 2017.
- 55% of pre-clearing habitat for threatened wetland and Melaleuca open woodland flora was cleared by 2017.
- 52% of pre-clearing habitat for threatened rainforest and scrub flora was cleared by 2017.
- Only threatened heath and other coastal community flora retained more than half (58%) of its pre-clear habitat extent by 2017.
SEQ land clearing between 1997 and 2017 was primarily for pasture development and forestry.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
Wet Tropics
Pre-clearing habitat extent for 206 currently threatened flora species was modelled for the Wet Tropics Queensland (WET) bioregion. Prior to land clearing, WET provided habitat for:
- 30 threatened eucalypt forest and woodland species
- 155 threatened rainforest and scrub species
- 12 threatened wetland and Melaleuca open woodland species
- 8 threatened heath and other coastal community species.
The trend in habitat extent between 1997 and 2017 in WET is one of ongoing, incremental loss of habitat for all threatened flora groups.
- Pre-clearing habitat for threatened eucalypt forest and woodland flora (90%), rainforest and scrub flora (79%) and heath and other coastal community flora (95%) remained largely uncleared by 2017.
- Almost one-third (31%) of habitat for threatened wetland and Melaleuca open woodland species had been cleared by 2017.
WET land clearing between 1997 and 2017 was primarily for forestry and pasture development.
It should be noted that some threatened flora species may be able to utilise non-remnant vegetation and that threatening processes such as habitat degradation, loss of habitat connectivity, disease, herbivory, invasive species, grazing and inappropriate fire management place significant additional pressure on threatened flora in both remnant and non-remnant habitat.
More information:
Relevant Sustainable Development Goals’ targets
Area of Queensland pre-clear threatened flora habitat and 2017 remnant habitat by species group
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 40,354,737 | 27,347,944 |
|---|
| Rainforest and scrub | 28,572,169 | 17,096,933 |
|---|
| Acacia forest, woodland and shrubland | 23,364,932 | 13,984,568 |
|---|
| Wetland and Melaleuca open woodland | 29,595,549 | 19,122,930 |
|---|
| Grassland and forbland | 9,691,262 | 3,846,949 |
|---|
| Heath and other coastal community | 3,388,734 | 2,246,022
|
|---|
Proportion of Queensland pre-clear threatened flora habitat that is remnant and non-remnant habitat, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 27,347,944 | 13,006,793 |
|---|
| Rainforest and scrub | 17,096,933 | 11,475,236 |
|---|
| Acacia forest, woodland and shrubland | 13,984,568 | 9,380,364 |
|---|
| Wetland and Melaleuca open woodland | 19,122,930 | 10,472,619 |
|---|
| Grassland and forbland | 3,846,949 | 5,844,313 |
|---|
| Heath and other coastal community | 2,246,022 | 1,142,712
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat
| Year | Habitat (hectares)
|
|---|
| 1997 | 28,066,294 |
|---|
| 1999 | 27,851,423 |
|---|
| 2000 | 27,716,313 |
|---|
| 2001 | 27,673,046 |
|---|
| 2003 | 27,589,204 |
|---|
| 2005 | 27,528,186 |
|---|
| 2006 | 27,491,615 |
|---|
| 2007 | 27,464,707 |
|---|
| 2009 | 27,443,838 |
|---|
| 2011 | 27,432,286 |
|---|
| 2013 | 27,409,228 |
|---|
| 2015 | 27,388,165 |
|---|
| 2017 | 27,347,944
|
|---|
Proportion of pre-clear threatened eucalypt forest and woodland habitat by bioregion
| Region | Pre-clear
|
|---|
| Brigalow Belt | 17,641,021 |
|---|
| Channel Country | 314 |
|---|
| Central Queensland Coast | 830,240 |
|---|
| Cape York Peninsula | 1,891,965 |
|---|
| Desert Uplands | 1,211,761 |
|---|
| Gulf Plains | 1,948,246 |
|---|
| Einasleigh Uplands | 5,623,492 |
|---|
| Mitchell Grass Downs | 1,342,229 |
|---|
| Mulga Lands | 698,295 |
|---|
| New England Tableland | 717,064 |
|---|
| Northwest Highlands | 2,077,066 |
|---|
| Southeast Queensland | 5,672,628 |
|---|
| Wet Tropics | 700,414
|
|---|
Trend in threatened rainforest and scrub habitat
| Year | Habitat (hectares)
|
|---|
| 1997 | 17,657,054 |
|---|
| 1999 | 17,469,984 |
|---|
| 2000 | 17,358,089 |
|---|
| 2001 | 17,326,649 |
|---|
| 2003 | 17,248,400 |
|---|
| 2005 | 17,199,484 |
|---|
| 2006 | 17,184,415 |
|---|
| 2007 | 17,164,476 |
|---|
| 2009 | 17,150,216 |
|---|
| 2011 | 17,140,894 |
|---|
| 2013 | 17,130,519 |
|---|
| 2015 | 17,119,659 |
|---|
| 2017 | 17,096,933
|
|---|
Proportion of pre-clear threatened rainforest and scrub habitat by bioregion
| Region | Pre-clear
|
|---|
| Brigalow Belt | 11,936,055 |
|---|
| Channel Country | 0 |
|---|
| Central Queensland Coast | 1,025,594 |
|---|
| Cape York Peninsula | 3,947,314 |
|---|
| Desert Uplands | 4,950 |
|---|
| Gulf Plains | 471,884 |
|---|
| Einasleigh Uplands | 3,727,701 |
|---|
| Mitchell Grass Downs | 101,907 |
|---|
| Mulga Lands | 465,104 |
|---|
| New England Tableland | 384,530 |
|---|
| Northwest Highlands | 0 |
|---|
| Southeast Queensland | 4,926,660 |
|---|
| Wet Tropics | 1,580,470
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat
| Year | Habitat (hectares)
|
|---|
| 1997 | 14,599,945 |
|---|
| 1999 | 14,476,693 |
|---|
| 2000 | 14,363,780 |
|---|
| 2001 | 14,341,588 |
|---|
| 2003 | 14,224,375 |
|---|
| 2005 | 14,148,215 |
|---|
| 2006 | 14,088,624 |
|---|
| 2007 | 14,072,046 |
|---|
| 2009 | 14,057,961 |
|---|
| 2011 | 14,045,607 |
|---|
| 2013 | 14,036,057 |
|---|
| 2015 | 14,013,060 |
|---|
| 2017 | 13,984,568
|
|---|
Proportion of pre-clear threatened acacia forest, woodland and shrubland habitat by bioregion
| Region | Pre-clear
|
|---|
| Brigalow Belt | 9,944,484 |
|---|
| Channel Country | 1,928,367 |
|---|
| Central Queensland Coast | 1,011 |
|---|
| Cape York Peninsula | 0 |
|---|
| Desert Uplands | 751,115 |
|---|
| Gulf Plains | 575,003 |
|---|
| Einasleigh Uplands | 494,365 |
|---|
| Mitchell Grass Downs | 4,781,477 |
|---|
| Mulga Lands | 4,255,952 |
|---|
| New England Tableland | 37,053 |
|---|
| Northwest Highlands | 50,715 |
|---|
| Southeast Queensland | 545,391 |
|---|
| Wet Tropics | 0
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat
| Year | Habitat (hectares)
|
|---|
| 1997 | 19,938,902 |
|---|
| 1999 | 19,730,329 |
|---|
| 2000 | 19,583,029 |
|---|
| 2001 | 19,531,258 |
|---|
| 2003 | 19,385,320 |
|---|
| 2005 | 19,313,361 |
|---|
| 2006 | 19,268,971 |
|---|
| 2007 | 19,245,868 |
|---|
| 2009 | 19,231,643 |
|---|
| 2011 | 19,219,353 |
|---|
| 2013 | 19,204,661 |
|---|
| 2015 | 19,177,696 |
|---|
| 2017 | 19,122,930
|
|---|
Proportion of pre-clear threatened wetland and melaleuca open woodland habitat by bioregion
| Region | Pre-clear
|
|---|
| Brigalow Belt | 11,549,100 |
|---|
| Channel Country | 949,721 |
|---|
| Central Queensland Coast | 426,441 |
|---|
| Cape York Peninsula | 2,799,142 |
|---|
| Desert Uplands | 1,858,528 |
|---|
| Gulf Plains | 700,336 |
|---|
| Einasleigh Uplands | 853,742 |
|---|
| Mitchell Grass Downs | 3,192,584 |
|---|
| Mulga Lands | 3,201,884 |
|---|
| New England Tableland | 228,901 |
|---|
| Northwest Highlands | 0 |
|---|
| Southeast Queensland | 2,632,373 |
|---|
| Wet Tropics | 1,202,796
|
|---|
Trend in threatened grassland and forbland habitat
| Year | Habitat (hectares)
|
|---|
| 1997 | 4,059,649 |
|---|
| 1999 | 3,982,720 |
|---|
| 2000 | 3,944,147 |
|---|
| 2001 | 3,932,662 |
|---|
| 2003 | 3,912,602 |
|---|
| 2005 | 3,894,584 |
|---|
| 2006 | 3,885,811 |
|---|
| 2007 | 3,879,280 |
|---|
| 2009 | 3,871,189 |
|---|
| 2011 | 3,867,706 |
|---|
| 2013 | 3,861,858 |
|---|
| 2015 | 3,856,649 |
|---|
| 2017 | 3,846,949
|
|---|
Proportion of pre-clear threatened grassland and forbland habitat by bioregion
| Region | Pre-clear
|
|---|
| Brigalow Belt | 6,200,331 |
|---|
| Channel Country | 2,199 |
|---|
| Central Queensland Coast | 6 |
|---|
| Cape York Peninsula | 907 |
|---|
| Desert Uplands | 4,826 |
|---|
| Gulf Plains | 1,031 |
|---|
| Einasleigh Uplands | 221,445 |
|---|
| Mitchell Grass Downs | 410,356 |
|---|
| Mulga Lands | 164,506 |
|---|
| New England Tableland | 392,906 |
|---|
| Northwest Highlands | 0 |
|---|
| Southeast Queensland | 2,292,751 |
|---|
| Wet Tropics | 0
|
|---|
Trend in threatened heath and other coastal community habitat
| Year | Habitat (hectares)
|
|---|
| 1997 | 2,297,843 |
|---|
| 1999 | 2,281,821 |
|---|
| 2000 | 2,270,876 |
|---|
| 2001 | 2,268,391 |
|---|
| 2003 | 2,260,517 |
|---|
| 2005 | 2,254,734 |
|---|
| 2006 | 2,253,090 |
|---|
| 2007 | 2,250,580 |
|---|
| 2009 | 2,247,709 |
|---|
| 2011 | 2,246,295 |
|---|
| 2013 | 2,244,583 |
|---|
| 2015 | 2,248,096 |
|---|
| 2017 | 2,246,022
|
|---|
Proportion of pre-clear threatened heath and other coastal community habitat by bioregion
| Region | Pre-clear
|
|---|
| Brigalow Belt | 952,834 |
|---|
| Channel Country | 0 |
|---|
| Central Queensland Coast | 26,005 |
|---|
| Cape York Peninsula | 1,936 |
|---|
| Desert Uplands | 135 |
|---|
| Gulf Plains | 0 |
|---|
| Einasleigh Uplands | 219,990 |
|---|
| Mitchell Grass Downs | 0 |
|---|
| Mulga Lands | 124 |
|---|
| New England Tableland | 140,708 |
|---|
| Northwest Highlands | 0 |
|---|
| Southeast Queensland | 1,922,919 |
|---|
| Wet Tropics | 124,083
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Brigalow Belt
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 17,641,021 | 9,189,221 |
|---|
| Rainforest and scrub | 11,936,055 | 4,437,565 |
|---|
| Acacia forest, woodland and shrubland | 9,944,484 | 2,315,448 |
|---|
| Wetland and Melaleuca open woodland | 11,549,100 | 4,049,162 |
|---|
| Grassland and forbland | 6,200,331 | 2,208,185 |
|---|
| Heath and other coastal community | 952,834 | 699,405
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Brigalow Belt, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 9,189,221 | 8,451,800 |
|---|
| Rainforest and scrub | 4,437,565 | 7,498,490 |
|---|
| Acacia forest, woodland and shrubland | 2,315,448 | 7,629,036 |
|---|
| Wetland and Melaleuca open woodland | 4,049,162 | 7,499,938 |
|---|
| Grassland and forbland | 2,208,185 | 3,992,146 |
|---|
| Heath and other coastal community | 699,405 | 253,429
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Brigalow Belt
| Year | Habitat (hectares)
|
|---|
| 1997 | 9,674,545 |
|---|
| 1999 | 9,508,818 |
|---|
| 2000 | 9,423,059 |
|---|
| 2001 | 9,395,083 |
|---|
| 2003 | 9,343,530 |
|---|
| 2005 | 9,304,142 |
|---|
| 2006 | 9,285,136 |
|---|
| 2007 | 9,268,313 |
|---|
| 2009 | 9,256,298 |
|---|
| 2011 | 9,250,184 |
|---|
| 2013 | 9,234,905 |
|---|
| 2015 | 9,214,917 |
|---|
| 2017 | 9,189,221
|
|---|
Trend in threatened rainforest and scrub habitat in the Brigalow Belt
| Year | Habitat (hectares)
|
|---|
| 1997 | 4,795,201 |
|---|
| 1999 | 4,661,808 |
|---|
| 2000 | 4,590,842 |
|---|
| 2001 | 4,570,810 |
|---|
| 2003 | 4,519,808 |
|---|
| 2005 | 4,488,237 |
|---|
| 2006 | 4,480,358 |
|---|
| 2007 | 4,471,691 |
|---|
| 2009 | 4,466,595 |
|---|
| 2011 | 4,463,312 |
|---|
| 2013 | 4,459,119 |
|---|
| 2015 | 4,448,232 |
|---|
| 2017 | 4,437,565
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Brigalow Belt
| Year | Habitat (hectares)
|
|---|
| 1997 | 2,565,513 |
|---|
| 1999 | 2,477,050 |
|---|
| 2000 | 2,413,363 |
|---|
| 2001 | 2,399,459 |
|---|
| 2003 | 2,373,018 |
|---|
| 2005 | 2,354,288 |
|---|
| 2006 | 2,345,856 |
|---|
| 2007 | 2,341,928 |
|---|
| 2009 | 2,336,371 |
|---|
| 2011 | 2,333,370 |
|---|
| 2013 | 2,329,072 |
|---|
| 2015 | 2,323,227 |
|---|
| 2017 | 2,315,448
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Brigalow Belt
| Year | Habitat (hectares)
|
|---|
| 1997 | 4,478,398 |
|---|
| 1999 | 4,333,576 |
|---|
| 2000 | 4,250,273 |
|---|
| 2001 | 4,224,798 |
|---|
| 2003 | 4,175,322 |
|---|
| 2005 | 4,137,582 |
|---|
| 2006 | 4,122,717 |
|---|
| 2007 | 4,105,484 |
|---|
| 2009 | 4,097,652 |
|---|
| 2011 | 4,093,216 |
|---|
| 2013 | 4,085,159 |
|---|
| 2015 | 4,074,577 |
|---|
| 2017 | 4,049,162
|
|---|
Trend in threatened grassland and forbland habitat in the Brigalow Belt
| Year | Habitat (hectares)
|
|---|
| 1997 | 2,368,896 |
|---|
| 1999 | 2,307,951 |
|---|
| 2000 | 2,278,463 |
|---|
| 2001 | 2,269,518 |
|---|
| 2003 | 2,255,134 |
|---|
| 2005 | 2,241,877 |
|---|
| 2006 | 2,236,373 |
|---|
| 2007 | 2,231,769 |
|---|
| 2009 | 2,226,332 |
|---|
| 2011 | 2,224,284 |
|---|
| 2013 | 2,221,161 |
|---|
| 2015 | 2,215,553 |
|---|
| 2017 | 2,208,185
|
|---|
Trend in threatened heath and other coastal community habitat in the Brigalow Belt
| Year | Habitat (hectares)
|
|---|
| 1997 | 730,395 |
|---|
| 1999 | 720,205 |
|---|
| 2000 | 713,673 |
|---|
| 2001 | 712,529 |
|---|
| 2003 | 708,081 |
|---|
| 2005 | 705,012 |
|---|
| 2006 | 704,790 |
|---|
| 2007 | 704,193 |
|---|
| 2009 | 703,059 |
|---|
| 2011 | 702,629 |
|---|
| 2013 | 701,689 |
|---|
| 2015 | 700,395 |
|---|
| 2017 | 699,405
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Channel Country
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 314 | 314 |
|---|
| Rainforest and scrub | 0 | 0 |
|---|
| Acacia forest, woodland and shrubland | 1,928,367 | 1,926,035 |
|---|
| Wetland and Melaleuca open woodland | 949,721 | 947,298 |
|---|
| Grassland and forbland | 2,199 | 2,199 |
|---|
| Heath and other coastal community | 0 | 0
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Channel Country, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 314 | 0 |
|---|
| Rainforest and scrub | 0 | 0 |
|---|
| Acacia forest, woodland and shrubland | 1,926,035 | 2,332 |
|---|
| Wetland and Melaleuca open woodland | 947,298 | 2,423 |
|---|
| Grassland and forbland | 2,199 | 0 |
|---|
| Heath and other coastal community | 0 | 0
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Channel Country
| Year | Habitat (hectares)
|
|---|
| 1997 | 314 |
|---|
| 1999 | 314 |
|---|
| 2000 | 314 |
|---|
| 2001 | 314 |
|---|
| 2003 | 314 |
|---|
| 2005 | 314 |
|---|
| 2006 | 314 |
|---|
| 2007 | 314 |
|---|
| 2009 | 314 |
|---|
| 2011 | 314 |
|---|
| 2013 | 314 |
|---|
| 2015 | 314 |
|---|
| 2017 | 314
|
|---|
Trend in threatened rainforest and scrub habitat in the Channel Country
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Channel Country
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,926,743 |
|---|
| 1999 | 1,926,741 |
|---|
| 2000 | 1,926,741 |
|---|
| 2001 | 1,926,741 |
|---|
| 2003 | 1,926,738 |
|---|
| 2005 | 1,926,606 |
|---|
| 2006 | 1,926,573 |
|---|
| 2007 | 1,926,202 |
|---|
| 2009 | 1,926,200 |
|---|
| 2011 | 1,926,098 |
|---|
| 2013 | 1,926,098 |
|---|
| 2015 | 1,926,097 |
|---|
| 2017 | 1,926,035
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Channel Country
| Year | Habitat (hectares)
|
|---|
| 1997 | 948,470 |
|---|
| 1999 | 948,470 |
|---|
| 2000 | 948,470 |
|---|
| 2001 | 948,467 |
|---|
| 2003 | 948,038 |
|---|
| 2005 | 947,948 |
|---|
| 2006 | 947,737 |
|---|
| 2007 | 947,645 |
|---|
| 2009 | 947,645 |
|---|
| 2011 | 947,567 |
|---|
| 2013 | 947,567 |
|---|
| 2015 | 947,520 |
|---|
| 2017 | 947,298
|
|---|
Trend in threatened grassland and forbland habitat in the Channel Country
| Year | Habitat (hectares)
|
|---|
| 1997 | 2,199 |
|---|
| 1999 | 2,199 |
|---|
| 2000 | 2,199 |
|---|
| 2001 | 2,199 |
|---|
| 2003 | 2,199 |
|---|
| 2005 | 2,199 |
|---|
| 2006 | 2,199 |
|---|
| 2007 | 2,199 |
|---|
| 2009 | 2,199 |
|---|
| 2011 | 2,199 |
|---|
| 2013 | 2,199 |
|---|
| 2015 | 2,199 |
|---|
| 2017 | 2,199
|
|---|
Trend in threatened heath and other coastal community habitat in the Channel Country
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Central Queensland Coast
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 830,240 | 718,297 |
|---|
| Rainforest and scrub | 1,025,594 | 723,108 |
|---|
| Acacia forest, woodland and shrubland | 1,011 | 886 |
|---|
| Wetland and Melaleuca open woodland | 426,441 | 323,029 |
|---|
| Grassland and forbland | 6 | 5 |
|---|
| Heath and other coastal community | 26,005 | 25,461
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Central Queensland Coast, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 718,297 | 111,943 |
|---|
| Rainforest and scrub | 723,108 | 302,486 |
|---|
| Acacia forest, woodland and shrubland | 886 | 125 |
|---|
| Wetland and Melaleuca open woodland | 323,029 | 103,412 |
|---|
| Grassland and forbland | 5 | 1 |
|---|
| Heath and other coastal community | 25,461 | 544
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Central Queensland Coast
| Year | Habitat (hectares)
|
|---|
| 1997 | 728,331 |
|---|
| 1999 | 726,728 |
|---|
| 2000 | 724,998 |
|---|
| 2001 | 724,431 |
|---|
| 2003 | 723,469 |
|---|
| 2005 | 722,282 |
|---|
| 2006 | 721,332 |
|---|
| 2007 | 720,721 |
|---|
| 2009 | 720,244 |
|---|
| 2011 | 720,173 |
|---|
| 2013 | 720,023 |
|---|
| 2015 | 719,380 |
|---|
| 2017 | 718,297
|
|---|
Trend in threatened rainforest and scrub habitat in the Central Queensland Coast
| Year | Habitat (hectares)
|
|---|
| 1997 | 735,547 |
|---|
| 1999 | 732,766 |
|---|
| 2000 | 729,972 |
|---|
| 2001 | 728,902 |
|---|
| 2003 | 727,957 |
|---|
| 2005 | 726,754 |
|---|
| 2006 | 726,086 |
|---|
| 2007 | 725,526 |
|---|
| 2009 | 724,856 |
|---|
| 2011 | 724,716 |
|---|
| 2013 | 724,314 |
|---|
| 2015 | 724,003 |
|---|
| 2017 | 723,108
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Central Queensland Coast
| Year | Habitat (hectares)
|
|---|
| 1997 | 886 |
|---|
| 1999 | 886 |
|---|
| 2000 | 886 |
|---|
| 2001 | 886 |
|---|
| 2003 | 886 |
|---|
| 2005 | 886 |
|---|
| 2006 | 886 |
|---|
| 2007 | 886 |
|---|
| 2009 | 886 |
|---|
| 2011 | 886 |
|---|
| 2013 | 886 |
|---|
| 2015 | 886 |
|---|
| 2017 | 886
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Central Queensland Coast
| Year | Habitat (hectares)
|
|---|
| 1997 | 329,111 |
|---|
| 1999 | 328,013 |
|---|
| 2000 | 326,706 |
|---|
| 2001 | 326,418 |
|---|
| 2003 | 325,730 |
|---|
| 2005 | 325,061 |
|---|
| 2006 | 324,612 |
|---|
| 2007 | 324,437 |
|---|
| 2009 | 324,231 |
|---|
| 2011 | 324,182 |
|---|
| 2013 | 324,134 |
|---|
| 2015 | 323,636 |
|---|
| 2017 | 323,029
|
|---|
Trend in threatened grassland and forbland habitat in the Central Queensland Coast
| Year | Habitat (hectares)
|
|---|
| 1997 | 5 |
|---|
| 1999 | 5 |
|---|
| 2000 | 5 |
|---|
| 2001 | 5 |
|---|
| 2003 | 5 |
|---|
| 2005 | 5 |
|---|
| 2006 | 5 |
|---|
| 2007 | 5 |
|---|
| 2009 | 5 |
|---|
| 2011 | 5 |
|---|
| 2013 | 5 |
|---|
| 2015 | 5 |
|---|
| 2017 | 5
|
|---|
Trend in threatened heath and other coastal community habitat in the Central Queensland Coast
| Year | Habitat (hectares)
|
|---|
| 1997 | 25,485 |
|---|
| 1999 | 25,485 |
|---|
| 2000 | 25,485 |
|---|
| 2001 | 25,485 |
|---|
| 2003 | 25,483 |
|---|
| 2005 | 25,479 |
|---|
| 2006 | 25,462 |
|---|
| 2007 | 25,462 |
|---|
| 2009 | 25,462 |
|---|
| 2011 | 25,462 |
|---|
| 2013 | 25,462 |
|---|
| 2015 | 25,462 |
|---|
| 2017 | 25,461
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Cape York Peninsula
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 1,891,965 | 1,880,858 |
|---|
| Rainforest and scrub | 3,947,314 | 3,882,869 |
|---|
| Acacia forest, woodland and shrubland | 0 | 0 |
|---|
| Wetland and Melaleuca open woodland | 2,799,142 | 2,785,389 |
|---|
| Grassland and forbland | 907 | 738 |
|---|
| Heath and other coastal community | 1,936 | 1,917
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Cape York Peninsula, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 1,880,858 | 11,107 |
|---|
| Rainforest and scrub | 3,882,869 | 64,445 |
|---|
| Acacia forest, woodland and shrubland | 0 | 0 |
|---|
| Wetland and Melaleuca open woodland | 2,785,389 | 13,753 |
|---|
| Grassland and forbland | 738 | 169 |
|---|
| Heath and other coastal community | 1,917 | 19
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Cape York Peninsula
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,882,053 |
|---|
| 1999 | 1,881,830 |
|---|
| 2000 | 1,881,638 |
|---|
| 2001 | 1,881,614 |
|---|
| 2003 | 1,881,484 |
|---|
| 2005 | 1,881,264 |
|---|
| 2006 | 1,881,214 |
|---|
| 2007 | 1,881,153 |
|---|
| 2009 | 1,881,099 |
|---|
| 2011 | 1,881,050 |
|---|
| 2013 | 1,880,961 |
|---|
| 2015 | 1,880,917 |
|---|
| 2017 | 1,880,858
|
|---|
Trend in threatened rainforest and scrub habitat in the Cape York Peninsula
| Year | Habitat (hectares)
|
|---|
| 1997 | 3,904,599 |
|---|
| 1999 | 3,903,496 |
|---|
| 2000 | 3,901,964 |
|---|
| 2001 | 3,901,061 |
|---|
| 2003 | 3,900,470 |
|---|
| 2005 | 3,898,999 |
|---|
| 2006 | 3,898,028 |
|---|
| 2007 | 3,896,248 |
|---|
| 2009 | 3,893,514 |
|---|
| 2011 | 3,891,729 |
|---|
| 2013 | 3,889,098 |
|---|
| 2015 | 3,886,689 |
|---|
| 2017 | 3,882,869
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Cape York Peninsula
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Cape York Peninsula
| Year | Habitat (hectares)
|
|---|
| 1997 | 2,788,277 |
|---|
| 1999 | 2,788,170 |
|---|
| 2000 | 2,787,824 |
|---|
| 2001 | 2,787,815 |
|---|
| 2003 | 2,787,689 |
|---|
| 2005 | 2,787,546 |
|---|
| 2006 | 2,787,517 |
|---|
| 2007 | 2,787,421 |
|---|
| 2009 | 2,787,271 |
|---|
| 2011 | 2,787,251 |
|---|
| 2013 | 2,787,194 |
|---|
| 2015 | 2,785,623 |
|---|
| 2017 | 2,785,389
|
|---|
Trend in threatened grassland and forbland habitat in the Cape York Peninsula
| Year | Habitat (hectares)
|
|---|
| 1997 | 738 |
|---|
| 1999 | 738 |
|---|
| 2000 | 738 |
|---|
| 2001 | 738 |
|---|
| 2003 | 738 |
|---|
| 2005 | 738 |
|---|
| 2006 | 738 |
|---|
| 2007 | 738 |
|---|
| 2009 | 738 |
|---|
| 2011 | 738 |
|---|
| 2013 | 738 |
|---|
| 2015 | 738 |
|---|
| 2017 | 738
|
|---|
Trend in threatened heath and other coastal community habitat in the Cape York Peninsula
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,917 |
|---|
| 1999 | 1,917 |
|---|
| 2000 | 1,917 |
|---|
| 2001 | 1,917 |
|---|
| 2003 | 1,917 |
|---|
| 2005 | 1,917 |
|---|
| 2006 | 1,917 |
|---|
| 2007 | 1,917 |
|---|
| 2009 | 1,917 |
|---|
| 2011 | 1,917 |
|---|
| 2013 | 1,917 |
|---|
| 2015 | 1,917 |
|---|
| 2017 | 1,917
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Desert Uplands
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 1,211,761 | 929,291 |
|---|
| Rainforest and scrub | 4,950 | 4,448 |
|---|
| Acacia forest, woodland and shrubland | 751,115 | 586,424 |
|---|
| Wetland and Melaleuca open woodland | 1,858,528 | 1,493,961 |
|---|
| Grassland and forbland | 4,826 | 4,324 |
|---|
| Heath and other coastal community | 135 | 135
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Desert Uplands, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 929,291 | 282,470 |
|---|
| Rainforest and scrub | 4,448 | 502 |
|---|
| Acacia forest, woodland and shrubland | 586,424 | 164,691 |
|---|
| Wetland and Melaleuca open woodland | 1,493,961 | 364,567 |
|---|
| Grassland and forbland | 4,324 | 502 |
|---|
| Heath and other coastal community | 135 | 0
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Desert Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 993,281 |
|---|
| 1999 | 987,989 |
|---|
| 2000 | 970,815 |
|---|
| 2001 | 964,157 |
|---|
| 2003 | 948,479 |
|---|
| 2005 | 942,165 |
|---|
| 2006 | 933,849 |
|---|
| 2007 | 933,726 |
|---|
| 2009 | 933,216 |
|---|
| 2011 | 933,045 |
|---|
| 2013 | 932,287 |
|---|
| 2015 | 931,962 |
|---|
| 2017 | 929,291
|
|---|
Trend in threatened rainforest and scrub habitat in the Desert Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 4,518 |
|---|
| 1999 | 4,455 |
|---|
| 2000 | 4,454 |
|---|
| 2001 | 4,454 |
|---|
| 2003 | 4,454 |
|---|
| 2005 | 4,452 |
|---|
| 2006 | 4,452 |
|---|
| 2007 | 4,452 |
|---|
| 2009 | 4,452 |
|---|
| 2011 | 4,452 |
|---|
| 2013 | 4,452 |
|---|
| 2015 | 4,451 |
|---|
| 2017 | 4,448
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Desert Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 650,385 |
|---|
| 1999 | 640,739 |
|---|
| 2000 | 618,549 |
|---|
| 2001 | 614,785 |
|---|
| 2003 | 600,011 |
|---|
| 2005 | 593,670 |
|---|
| 2006 | 588,407 |
|---|
| 2007 | 588,405 |
|---|
| 2009 | 588,068 |
|---|
| 2011 | 587,972 |
|---|
| 2013 | 587,612 |
|---|
| 2015 | 587,571 |
|---|
| 2017 | 586,424
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Desert Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,628,145 |
|---|
| 1999 | 1,605,836 |
|---|
| 2000 | 1,576,424 |
|---|
| 2001 | 1,559,127 |
|---|
| 2003 | 1,526,119 |
|---|
| 2005 | 1,515,210 |
|---|
| 2006 | 1,506,497 |
|---|
| 2007 | 1,506,017 |
|---|
| 2009 | 1,505,084 |
|---|
| 2011 | 1,504,429 |
|---|
| 2013 | 1,502,309 |
|---|
| 2015 | 1,499,444 |
|---|
| 2017 | 1,493,961
|
|---|
Trend in threatened grassland and forbland habitat in the Desert Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 4,372 |
|---|
| 1999 | 4,337 |
|---|
| 2000 | 4,335 |
|---|
| 2001 | 4,334 |
|---|
| 2003 | 4,324 |
|---|
| 2005 | 4,324 |
|---|
| 2006 | 4,324 |
|---|
| 2007 | 4,324 |
|---|
| 2009 | 4,324 |
|---|
| 2011 | 4,324 |
|---|
| 2013 | 4,324 |
|---|
| 2015 | 4,324 |
|---|
| 2017 | 4,324
|
|---|
Trend in threatened heath and other coastal community habitat in the Desert Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 135 |
|---|
| 1999 | 135 |
|---|
| 2000 | 135 |
|---|
| 2001 | 135 |
|---|
| 2003 | 135 |
|---|
| 2005 | 135 |
|---|
| 2006 | 135 |
|---|
| 2007 | 135 |
|---|
| 2009 | 135 |
|---|
| 2011 | 135 |
|---|
| 2013 | 135 |
|---|
| 2015 | 135 |
|---|
| 2017 | 135
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Gulf Plains
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 1,948,246 | 1,944,540 |
|---|
| Rainforest and scrub | 471,884 | 465,946 |
|---|
| Acacia forest, woodland and shrubland | 575,003 | 553,999 |
|---|
| Wetland and Melaleuca open woodland | 700,336 | 692,563 |
|---|
| Grassland and forbland | 1,031 | 1,026 |
|---|
| Heath and other coastal community | 0 | 0
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Gulf Plains, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 1,944,540 | 3,706 |
|---|
| Rainforest and scrub | 465,946 | 5,938 |
|---|
| Acacia forest, woodland and shrubland | 553,999 | 21,004 |
|---|
| Wetland and Melaleuca open woodland | 692,563 | 7,773 |
|---|
| Grassland and forbland | 1,026 | 5 |
|---|
| Heath and other coastal community | 0 | 0
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Gulf Plains
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,946,548 |
|---|
| 1999 | 1,946,311 |
|---|
| 2000 | 1,946,311 |
|---|
| 2001 | 1,946,216 |
|---|
| 2003 | 1,946,130 |
|---|
| 2005 | 1,946,024 |
|---|
| 2006 | 1,946,024 |
|---|
| 2007 | 1,946,109 |
|---|
| 2009 | 1,945,978 |
|---|
| 2011 | 1,945,978 |
|---|
| 2013 | 1,945,939 |
|---|
| 2015 | 1,945,010 |
|---|
| 2017 | 1,944,540
|
|---|
Trend in threatened rainforest and scrub habitat in the Gulf Plains
| Year | Habitat (hectares)
|
|---|
| 1997 | 467,023 |
|---|
| 1999 | 467,005 |
|---|
| 2000 | 467,005 |
|---|
| 2001 | 466,999 |
|---|
| 2003 | 466,982 |
|---|
| 2005 | 466,942 |
|---|
| 2006 | 466,018 |
|---|
| 2007 | 466,004 |
|---|
| 2009 | 465,986 |
|---|
| 2011 | 465,984 |
|---|
| 2013 | 465,967 |
|---|
| 2015 | 465,959 |
|---|
| 2017 | 465,946
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Gulf Plains
| Year | Habitat (hectares)
|
|---|
| 1997 | 560,212 |
|---|
| 1999 | 559,856 |
|---|
| 2000 | 559,499 |
|---|
| 2001 | 559,498 |
|---|
| 2003 | 559,297 |
|---|
| 2005 | 557,368 |
|---|
| 2006 | 555,226 |
|---|
| 2007 | 554,841 |
|---|
| 2009 | 554,761 |
|---|
| 2011 | 554,749 |
|---|
| 2013 | 554,648 |
|---|
| 2015 | 554,013 |
|---|
| 2017 | 553,999
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Gulf Plains
| Year | Habitat (hectares)
|
|---|
| 1997 | 697,814 |
|---|
| 1999 | 695,870 |
|---|
| 2000 | 695,870 |
|---|
| 2001 | 695,806 |
|---|
| 2003 | 695,712 |
|---|
| 2005 | 695,666 |
|---|
| 2006 | 695,666 |
|---|
| 2007 | 695,748 |
|---|
| 2009 | 695,495 |
|---|
| 2011 | 695,426 |
|---|
| 2013 | 695,260 |
|---|
| 2015 | 693,317 |
|---|
| 2017 | 692,563
|
|---|
Trend in threatened grassland and forbland habitat in the Gulf Plains
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,031 |
|---|
| 1999 | 1,031 |
|---|
| 2000 | 1,031 |
|---|
| 2001 | 1,028 |
|---|
| 2003 | 1,028 |
|---|
| 2005 | 1,026 |
|---|
| 2006 | 1,026 |
|---|
| 2007 | 1,026 |
|---|
| 2009 | 1,026 |
|---|
| 2011 | 1,026 |
|---|
| 2013 | 1,026 |
|---|
| 2015 | 1,026 |
|---|
| 2017 | 1,026
|
|---|
Trend in threatened heath and other coastal community habitat in the Gulf Plains
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Einasleigh Uplands
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 5,623,492 | 5,442,482 |
|---|
| Rainforest and scrub | 3,727,701 | 3,645,999 |
|---|
| Acacia forest, woodland and shrubland | 494,365 | 492,626 |
|---|
| Wetland and Melaleuca open woodland | 853,742 | 803,954 |
|---|
| Grassland and forbland | 221,445 | 217,317 |
|---|
| Heath and other coastal community | 219,990 | 219,083
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Einasleigh Uplands, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 5,442,482 | 181,010 |
|---|
| Rainforest and scrub | 3,645,999 | 81,702 |
|---|
| Acacia forest, woodland and shrubland | 492,626 | 1,739 |
|---|
| Wetland and Melaleuca open woodland | 803,954 | 49,788 |
|---|
| Grassland and forbland | 217,317 | 4,128 |
|---|
| Heath and other coastal community | 219,083 | 907
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Einasleigh Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 5,463,115 |
|---|
| 1999 | 5,459,533 |
|---|
| 2000 | 5,456,158 |
|---|
| 2001 | 5,454,943 |
|---|
| 2003 | 5,454,231 |
|---|
| 2005 | 5,452,423 |
|---|
| 2006 | 5,451,556 |
|---|
| 2007 | 5,448,591 |
|---|
| 2009 | 5,448,011 |
|---|
| 2011 | 5,447,783 |
|---|
| 2013 | 5,447,371 |
|---|
| 2015 | 5,446,195 |
|---|
| 2017 | 5,442,482
|
|---|
Trend in threatened rainforest and scrub habitat in the Einasleigh Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 3,658,643 |
|---|
| 1999 | 3,657,017 |
|---|
| 2000 | 3,655,407 |
|---|
| 2001 | 3,654,807 |
|---|
| 2003 | 3,654,168 |
|---|
| 2005 | 3,652,489 |
|---|
| 2006 | 3,652,214 |
|---|
| 2007 | 3,649,916 |
|---|
| 2009 | 3,649,577 |
|---|
| 2011 | 3,649,492 |
|---|
| 2013 | 3,649,206 |
|---|
| 2015 | 3,648,906 |
|---|
| 2017 | 3,645,999
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Einasleigh Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 492,674 |
|---|
| 1999 | 492,674 |
|---|
| 2000 | 492,673 |
|---|
| 2001 | 492,654 |
|---|
| 2003 | 492,646 |
|---|
| 2005 | 492,642 |
|---|
| 2006 | 492,642 |
|---|
| 2007 | 492,642 |
|---|
| 2009 | 492,637 |
|---|
| 2011 | 492,629 |
|---|
| 2013 | 492,629 |
|---|
| 2015 | 492,629 |
|---|
| 2017 | 492,626
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Einasleigh Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 809,212 |
|---|
| 1999 | 808,613 |
|---|
| 2000 | 807,834 |
|---|
| 2001 | 807,460 |
|---|
| 2003 | 807,161 |
|---|
| 2005 | 805,917 |
|---|
| 2006 | 805,000 |
|---|
| 2007 | 804,828 |
|---|
| 2009 | 804,691 |
|---|
| 2011 | 804,566 |
|---|
| 2013 | 804,515 |
|---|
| 2015 | 804,309 |
|---|
| 2017 | 803,954
|
|---|
Trend in threatened grassland and forbland habitat in the Einasleigh Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 218,571 |
|---|
| 1999 | 218,485 |
|---|
| 2000 | 218,247 |
|---|
| 2001 | 218,220 |
|---|
| 2003 | 217,858 |
|---|
| 2005 | 217,835 |
|---|
| 2006 | 217,832 |
|---|
| 2007 | 217,832 |
|---|
| 2009 | 217,832 |
|---|
| 2011 | 217,832 |
|---|
| 2013 | 217,832 |
|---|
| 2015 | 217,815 |
|---|
| 2017 | 217,317
|
|---|
Trend in threatened heath and other coastal community habitat in the Einasleigh Uplands
| Year | Habitat (hectares)
|
|---|
| 1997 | 219,208 |
|---|
| 1999 | 219,188 |
|---|
| 2000 | 219,115 |
|---|
| 2001 | 219,115 |
|---|
| 2003 | 219,114 |
|---|
| 2005 | 219,111 |
|---|
| 2006 | 219,111 |
|---|
| 2007 | 219,109 |
|---|
| 2009 | 219,108 |
|---|
| 2011 | 219,107 |
|---|
| 2013 | 219,093 |
|---|
| 2015 | 219,086 |
|---|
| 2017 | 219,083
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Mitchell Grass Downs
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 1,342,229 | 1,273,899 |
|---|
| Rainforest and scrub | 101,907 | 41,229 |
|---|
| Acacia forest, woodland and shrubland | 4,781,477 | 4,126,011 |
|---|
| Wetland and Melaleuca open woodland | 3,192,584 | 2,977,217 |
|---|
| Grassland and forbland | 410,356 | 389,779 |
|---|
| Heath and other coastal community | 0 | 0
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Mitchell Grass Downs, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 1,273,899 | 68,330 |
|---|
| Rainforest and scrub | 41,229 | 60,678 |
|---|
| Acacia forest, woodland and shrubland | 4,126,011 | 655,466 |
|---|
| Wetland and Melaleuca open woodland | 2,977,217 | 215,367 |
|---|
| Grassland and forbland | 389,779 | 20,577 |
|---|
| Heath and other coastal community | 0 | 0
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Mitchell Grass Downs
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,299,610 |
|---|
| 1999 | 1,291,604 |
|---|
| 2000 | 1,285,874 |
|---|
| 2001 | 1,285,388 |
|---|
| 2003 | 1,284,667 |
|---|
| 2005 | 1,282,915 |
|---|
| 2006 | 1,281,770 |
|---|
| 2007 | 1,281,556 |
|---|
| 2009 | 1,280,230 |
|---|
| 2011 | 1,279,606 |
|---|
| 2013 | 1,276,403 |
|---|
| 2015 | 1,275,821 |
|---|
| 2017 | 1,273,899
|
|---|
Trend in threatened rainforest and scrub habitat in the Mitchell Grass Downs
| Year | Habitat (hectares)
|
|---|
| 1997 | 59,085 |
|---|
| 1999 | 52,464 |
|---|
| 2000 | 45,913 |
|---|
| 2001 | 43,839 |
|---|
| 2003 | 42,625 |
|---|
| 2005 | 42,016 |
|---|
| 2006 | 41,865 |
|---|
| 2007 | 41,814 |
|---|
| 2009 | 41,774 |
|---|
| 2011 | 41,734 |
|---|
| 2013 | 41,697 |
|---|
| 2015 | 41,647 |
|---|
| 2017 | 41,229
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Mitchell Grass Downs
| Year | Habitat (hectares)
|
|---|
| 1997 | 4,229,717 |
|---|
| 1999 | 4,213,947 |
|---|
| 2000 | 4,197,176 |
|---|
| 2001 | 4,194,334 |
|---|
| 2003 | 4,178,546 |
|---|
| 2005 | 4,164,822 |
|---|
| 2006 | 4,160,826 |
|---|
| 2007 | 4,157,461 |
|---|
| 2009 | 4,154,364 |
|---|
| 2011 | 4,147,500 |
|---|
| 2013 | 4,144,282 |
|---|
| 2015 | 4,134,271 |
|---|
| 2017 | 4,126,011
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Mitchell Grass Downs
| Year | Habitat (hectares)
|
|---|
| 1997 | 3,065,976 |
|---|
| 1999 | 3,049,215 |
|---|
| 2000 | 3,028,669 |
|---|
| 2001 | 3,025,607 |
|---|
| 2003 | 3,019,888 |
|---|
| 2005 | 3,010,662 |
|---|
| 2006 | 3,005,598 |
|---|
| 2007 | 3,004,594 |
|---|
| 2009 | 3,002,908 |
|---|
| 2011 | 2,998,282 |
|---|
| 2013 | 2,996,333 |
|---|
| 2015 | 2,983,333 |
|---|
| 2017 | 2,977,217
|
|---|
Trend in threatened grassland and forbland habitat in the Mitchell Grass Downs
| Year | Habitat (hectares)
|
|---|
| 1997 | 399,355 |
|---|
| 1999 | 397,988 |
|---|
| 2000 | 396,624 |
|---|
| 2001 | 396,281 |
|---|
| 2003 | 396,027 |
|---|
| 2005 | 394,755 |
|---|
| 2006 | 394,583 |
|---|
| 2007 | 394,364 |
|---|
| 2009 | 393,309 |
|---|
| 2011 | 392,941 |
|---|
| 2013 | 390,208 |
|---|
| 2015 | 390,195 |
|---|
| 2017 | 389,779
|
|---|
Trend in threatened heath and other coastal community habitat in the Mitchell Grass Downs
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Mulga Lands
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 698,295 | 442,847 |
|---|
| Rainforest and scrub | 465,104 | 108,078 |
|---|
| Acacia forest, woodland and shrubland | 4,255,952 | 3,842,833 |
|---|
| Wetland and Melaleuca open woodland | 3,201,884 | 2,942,786 |
|---|
| Grassland and forbland | 164,506 | 86,325 |
|---|
| Heath and other coastal community | 124 | 4
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Mulga Lands, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 442,847 | 255,448 |
|---|
| Rainforest and scrub | 108,078 | 357,026 |
|---|
| Acacia forest, woodland and shrubland | 3,842,833 | 413,119 |
|---|
| Wetland and Melaleuca open woodland | 2,942,786 | 259,098 |
|---|
| Grassland and forbland | 86,325 | 78,181 |
|---|
| Heath and other coastal community | 4 | 120
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Mulga Lands
| Year | Habitat (hectares)
|
|---|
| 1997 | 479,502 |
|---|
| 1999 | 467,812 |
|---|
| 2000 | 459,414 |
|---|
| 2001 | 456,872 |
|---|
| 2003 | 451,303 |
|---|
| 2005 | 448,440 |
|---|
| 2006 | 445,994 |
|---|
| 2007 | 445,670 |
|---|
| 2009 | 445,424 |
|---|
| 2011 | 444,837 |
|---|
| 2013 | 444,428 |
|---|
| 2015 | 443,710 |
|---|
| 2017 | 442,847
|
|---|
Trend in threatened rainforest and scrub habitat in the Mulga Lands
| Year | Habitat (hectares)
|
|---|
| 1997 | 182,856 |
|---|
| 1999 | 156,485 |
|---|
| 2000 | 138,361 |
|---|
| 2001 | 135,102 |
|---|
| 2003 | 118,706 |
|---|
| 2005 | 112,974 |
|---|
| 2006 | 112,285 |
|---|
| 2007 | 111,259 |
|---|
| 2009 | 110,574 |
|---|
| 2011 | 110,269 |
|---|
| 2013 | 109,646 |
|---|
| 2015 | 108,837 |
|---|
| 2017 | 108,078
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Mulga Lands
| Year | Habitat (hectares)
|
|---|
| 1997 | 4,028,021 |
|---|
| 1999 | 4,020,071 |
|---|
| 2000 | 4,011,332 |
|---|
| 2001 | 4,009,916 |
|---|
| 2003 | 3,950,523 |
|---|
| 2005 | 3,915,795 |
|---|
| 2006 | 3,876,283 |
|---|
| 2007 | 3,867,916 |
|---|
| 2009 | 3,863,286 |
|---|
| 2011 | 3,861,358 |
|---|
| 2013 | 3,859,940 |
|---|
| 2015 | 3,853,704 |
|---|
| 2017 | 3,842,833
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Mulga Lands
| Year | Habitat (hectares)
|
|---|
| 1997 | 3,061,475 |
|---|
| 1999 | 3,048,162 |
|---|
| 2000 | 3,041,266 |
|---|
| 2001 | 3,038,006 |
|---|
| 2003 | 2,985,784 |
|---|
| 2005 | 2,976,949 |
|---|
| 2006 | 2,964,567 |
|---|
| 2007 | 2,962,854 |
|---|
| 2009 | 2,961,571 |
|---|
| 2011 | 2,960,599 |
|---|
| 2013 | 2,959,100 |
|---|
| 2015 | 2,957,072 |
|---|
| 2017 | 2,942,786
|
|---|
Trend in threatened grassland and forbland habitat in the Mulga Lands
| Year | Habitat (hectares)
|
|---|
| 1997 | 104,227 |
|---|
| 1999 | 97,261 |
|---|
| 2000 | 93,582 |
|---|
| 2001 | 92,568 |
|---|
| 2003 | 90,435 |
|---|
| 2005 | 89,326 |
|---|
| 2006 | 87,270 |
|---|
| 2007 | 87,075 |
|---|
| 2009 | 86,984 |
|---|
| 2011 | 86,967 |
|---|
| 2013 | 86,869 |
|---|
| 2015 | 86,711 |
|---|
| 2017 | 86,325
|
|---|
Trend in threatened heath and other coastal community habitat in the Mulga Lands
| Year | Habitat (hectares)
|
|---|
| 1997 | 124 |
|---|
| 1999 | 10 |
|---|
| 2000 | 10 |
|---|
| 2001 | 10 |
|---|
| 2003 | 10 |
|---|
| 2005 | 4 |
|---|
| 2006 | 4 |
|---|
| 2007 | 4 |
|---|
| 2009 | 4 |
|---|
| 2011 | 4 |
|---|
| 2013 | 4 |
|---|
| 2015 | 4 |
|---|
| 2017 | 4
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the New England Tableland
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 717,064 | 267,561 |
|---|
| Rainforest and scrub | 384,530 | 149,782 |
|---|
| Acacia forest, woodland and shrubland | 37,053 | 10,378 |
|---|
| Wetland and Melaleuca open woodland | 228,901 | 104,121 |
|---|
| Grassland and forbland | 392,906 | 143,628 |
|---|
| Heath and other coastal community | 140,708 | 71,100
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the New England Tableland, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 267,561 | 449,503 |
|---|
| Rainforest and scrub | 149,782 | 234,748 |
|---|
| Acacia forest, woodland and shrubland | 10,378 | 26,675 |
|---|
| Wetland and Melaleuca open woodland | 104,121 | 124,780 |
|---|
| Grassland and forbland | 143,628 | 249,278 |
|---|
| Heath and other coastal community | 71,100 | 69,608
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the New England Tableland
| Year | Habitat (hectares)
|
|---|
| 1997 | 278,438 |
|---|
| 1999 | 274,178 |
|---|
| 2000 | 272,224 |
|---|
| 2001 | 271,968 |
|---|
| 2003 | 271,001 |
|---|
| 2005 | 270,434 |
|---|
| 2006 | 270,275 |
|---|
| 2007 | 270,049 |
|---|
| 2009 | 269,632 |
|---|
| 2011 | 269,508 |
|---|
| 2013 | 268,785 |
|---|
| 2015 | 268,202 |
|---|
| 2017 | 267,561
|
|---|
Trend in threatened rainforest and scrub habitat in the New England Tableland
| Year | Habitat (hectares)
|
|---|
| 1997 | 156,513 |
|---|
| 1999 | 154,423 |
|---|
| 2000 | 153,371 |
|---|
| 2001 | 153,211 |
|---|
| 2003 | 152,611 |
|---|
| 2005 | 152,320 |
|---|
| 2006 | 152,257 |
|---|
| 2007 | 152,107 |
|---|
| 2009 | 151,694 |
|---|
| 2011 | 151,596 |
|---|
| 2013 | 150,948 |
|---|
| 2015 | 150,277 |
|---|
| 2017 | 149,782
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the New England Tableland
| Year | Habitat (hectares)
|
|---|
| 1997 | 10,637 |
|---|
| 1999 | 10,593 |
|---|
| 2000 | 10,585 |
|---|
| 2001 | 10,580 |
|---|
| 2003 | 10,528 |
|---|
| 2005 | 10,523 |
|---|
| 2006 | 10,522 |
|---|
| 2007 | 10,515 |
|---|
| 2009 | 10,495 |
|---|
| 2011 | 10,495 |
|---|
| 2013 | 10,464 |
|---|
| 2015 | 10,420 |
|---|
| 2017 | 10,378
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the New England Tableland
| Year | Habitat (hectares)
|
|---|
| 1997 | 106,924 |
|---|
| 1999 | 105,613 |
|---|
| 2000 | 105,170 |
|---|
| 2001 | 105,122 |
|---|
| 2003 | 104,888 |
|---|
| 2005 | 104,615 |
|---|
| 2006 | 104,560 |
|---|
| 2007 | 104,484 |
|---|
| 2009 | 104,452 |
|---|
| 2011 | 104,429 |
|---|
| 2013 | 104,332 |
|---|
| 2015 | 104,270 |
|---|
| 2017 | 104,121
|
|---|
Trend in threatened grassland and forbland habitat in the New England Tableland
| Year | Habitat (hectares)
|
|---|
| 1997 | 148,588 |
|---|
| 1999 | 146,406 |
|---|
| 2000 | 145,519 |
|---|
| 2001 | 145,419 |
|---|
| 2003 | 145,001 |
|---|
| 2005 | 144,664 |
|---|
| 2006 | 144,585 |
|---|
| 2007 | 144,492 |
|---|
| 2009 | 144,314 |
|---|
| 2011 | 144,236 |
|---|
| 2013 | 144,053 |
|---|
| 2015 | 143,903 |
|---|
| 2017 | 143,628
|
|---|
Trend in threatened heath and other coastal community habitat in the New England Tableland
| Year | Habitat (hectares)
|
|---|
| 1997 | 73,066 |
|---|
| 1999 | 72,602 |
|---|
| 2000 | 72,094 |
|---|
| 2001 | 72,061 |
|---|
| 2003 | 71,763 |
|---|
| 2005 | 71,554 |
|---|
| 2006 | 71,527 |
|---|
| 2007 | 71,489 |
|---|
| 2009 | 71,472 |
|---|
| 2011 | 71,461 |
|---|
| 2013 | 71,443 |
|---|
| 2015 | 71,291 |
|---|
| 2017 | 71,100
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Northwest Highlands
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 2,077,066 | 2,073,731 |
|---|
| Rainforest and scrub | 0 | 0 |
|---|
| Acacia forest, woodland and shrubland | 50,715 | 50,411 |
|---|
| Wetland and Melaleuca open woodland | 0 | 0 |
|---|
| Grassland and forbland | 0 | 0 |
|---|
| Heath and other coastal community | 0 | 0
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Northwest Highlands, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 2,073,731 | 3,335 |
|---|
| Rainforest and scrub | 0 | 0 |
|---|
| Acacia forest, woodland and shrubland | 50,411 | 304 |
|---|
| Wetland and Melaleuca open woodland | 0 | 0 |
|---|
| Grassland and forbland | 0 | 0 |
|---|
| Heath and other coastal community | 0 | 0
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Northwest Highlands
| Year | Habitat (hectares)
|
|---|
| 1997 | 2,075,410 |
|---|
| 1999 | 2,075,066 |
|---|
| 2000 | 2,074,981 |
|---|
| 2001 | 2,074,981 |
|---|
| 2003 | 2,074,974 |
|---|
| 2005 | 2,074,959 |
|---|
| 2006 | 2,074,947 |
|---|
| 2007 | 2,074,838 |
|---|
| 2009 | 2,074,358 |
|---|
| 2011 | 2,074,291 |
|---|
| 2013 | 2,073,859 |
|---|
| 2015 | 2,073,780 |
|---|
| 2017 | 2,073,731
|
|---|
Trend in threatened rainforest and scrub habitat in the Northwest Highlands
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Northwest Highlands
| Year | Habitat (hectares)
|
|---|
| 1997 | 50,700 |
|---|
| 1999 | 50,700 |
|---|
| 2000 | 50,549 |
|---|
| 2001 | 50,543 |
|---|
| 2003 | 50,453 |
|---|
| 2005 | 50,411 |
|---|
| 2006 | 50,411 |
|---|
| 2007 | 50,411 |
|---|
| 2009 | 50,411 |
|---|
| 2011 | 50,411 |
|---|
| 2013 | 50,411 |
|---|
| 2015 | 50,411 |
|---|
| 2017 | 50,411
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Northwest Highlands
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Trend in threatened grassland and forbland habitat in the Northwest Highlands
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Trend in threatened heath and other coastal community habitat in the Northwest Highlands
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Southeast Queensland
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 5,672,628 | 2,553,791 |
|---|
| Rainforest and scrub | 4,926,660 | 2,384,485 |
|---|
| Acacia forest, woodland and shrubland | 545,391 | 79,518 |
|---|
| Wetland and Melaleuca open woodland | 2,632,373 | 1,171,983 |
|---|
| Grassland and forbland | 2,292,751 | 793,423 |
|---|
| Heath and other coastal community | 1,922,919 | 1,111,031
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Southeast Queensland, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 2,553,791 | 3,118,837 |
|---|
| Rainforest and scrub | 2,384,485 | 2,542,175 |
|---|
| Acacia forest, woodland and shrubland | 79,518 | 465,873 |
|---|
| Wetland and Melaleuca open woodland | 1,171,983 | 1,460,390 |
|---|
| Grassland and forbland | 793,423 | 1,499,328 |
|---|
| Heath and other coastal community | 1,111,031 | 811,888
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Southeast Queensland
| Year | Habitat (hectares)
|
|---|
| 1997 | 2,612,956 |
|---|
| 1999 | 2,599,253 |
|---|
| 2000 | 2,588,669 |
|---|
| 2001 | 2,585,320 |
|---|
| 2003 | 2,577,991 |
|---|
| 2005 | 2,571,282 |
|---|
| 2006 | 2,567,656 |
|---|
| 2007 | 2,562,351 |
|---|
| 2009 | 2,557,746 |
|---|
| 2011 | 2,554,166 |
|---|
| 2013 | 2,552,759 |
|---|
| 2015 | 2,556,816 |
|---|
| 2017 | 2,553,791
|
|---|
Trend in threatened rainforest and scrub habitat in the Southeast Queensland
| Year | Habitat (hectares)
|
|---|
| 1997 | 2,436,211 |
|---|
| 1999 | 2,423,918 |
|---|
| 2000 | 2,415,133 |
|---|
| 2001 | 2,412,112 |
|---|
| 2003 | 2,405,586 |
|---|
| 2005 | 2,399,623 |
|---|
| 2006 | 2,396,431 |
|---|
| 2007 | 2,391,270 |
|---|
| 2009 | 2,387,123 |
|---|
| 2011 | 2,383,677 |
|---|
| 2013 | 2,382,288 |
|---|
| 2015 | 2,387,131 |
|---|
| 2017 | 2,384,485
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Southeast Queensland
| Year | Habitat (hectares)
|
|---|
| 1997 | 84,455 |
|---|
| 1999 | 83,461 |
|---|
| 2000 | 82,428 |
|---|
| 2001 | 82,191 |
|---|
| 2003 | 81,729 |
|---|
| 2005 | 81,204 |
|---|
| 2006 | 80,993 |
|---|
| 2007 | 80,839 |
|---|
| 2009 | 80,481 |
|---|
| 2011 | 80,138 |
|---|
| 2013 | 80,015 |
|---|
| 2015 | 79,833 |
|---|
| 2017 | 79,518
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Southeast Queensland
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,188,847 |
|---|
| 1999 | 1,183,747 |
|---|
| 2000 | 1,180,113 |
|---|
| 2001 | 1,178,648 |
|---|
| 2003 | 1,175,403 |
|---|
| 2005 | 1,173,024 |
|---|
| 2006 | 1,171,611 |
|---|
| 2007 | 1,170,049 |
|---|
| 2009 | 1,168,427 |
|---|
| 2011 | 1,167,321 |
|---|
| 2013 | 1,166,841 |
|---|
| 2015 | 1,173,009 |
|---|
| 2017 | 1,171,983
|
|---|
Trend in threatened grassland and forbland habitat in the Southeast Queensland
| Year | Habitat (hectares)
|
|---|
| 1997 | 811,668 |
|---|
| 1999 | 806,319 |
|---|
| 2000 | 803,405 |
|---|
| 2001 | 802,352 |
|---|
| 2003 | 799,852 |
|---|
| 2005 | 797,835 |
|---|
| 2006 | 796,875 |
|---|
| 2007 | 795,457 |
|---|
| 2009 | 794,126 |
|---|
| 2011 | 793,154 |
|---|
| 2013 | 793,445 |
|---|
| 2015 | 794,182 |
|---|
| 2017 | 793,423
|
|---|
Trend in threatened heath and other coastal community habitat in the Southeast Queensland
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,129,271 |
|---|
| 1999 | 1,124,071 |
|---|
| 2000 | 1,120,289 |
|---|
| 2001 | 1,119,011 |
|---|
| 2003 | 1,115,909 |
|---|
| 2005 | 1,113,426 |
|---|
| 2006 | 1,112,097 |
|---|
| 2007 | 1,110,311 |
|---|
| 2009 | 1,108,598 |
|---|
| 2011 | 1,107,633 |
|---|
| 2013 | 1,106,925 |
|---|
| 2015 | 1,111,910 |
|---|
| 2017 | 1,111,031
|
|---|
Area of pre-clear threatened flora habitat and 2017 remnant habitat by species group in the Wet Tropics
| Flora Group | Pre-clear | Remnant
|
|---|
| Eucalypt forest and woodland | 700,414 | 631,113 |
|---|
| Rainforest and scrub | 1,580,470 | 1,253,424 |
|---|
| Acacia forest, woodland and shrubland | 0 | 0 |
|---|
| Wetland and Melaleuca open woodland | 1,202,796 | 831,467 |
|---|
| Grassland and forbland | 0 | 0 |
|---|
| Heath and other coastal community | 124,083 | 117,885
|
|---|
Proportion of pre-clear threatened flora habitat that is remnant and non-remnant habitat in the Wet Tropics, 2017
| Flora Group | Remnant | Non-remnant
|
|---|
| Eucalypt forest and woodland | 631,113 | 69,301 |
|---|
| Rainforest and scrub | 1,253,424 | 327,046 |
|---|
| Acacia forest, woodland and shrubland | 0 | 0 |
|---|
| Wetland and Melaleuca open woodland | 831,467 | 371,329 |
|---|
| Grassland and forbland | 0 | 0 |
|---|
| Heath and other coastal community | 117,885 | 6,198
|
|---|
Choose flora group to see habitat numbers:
Trend in threatened eucalypt forest and woodland habitat in the Wet Tropics
| Year | Habitat (hectares)
|
|---|
| 1997 | 632,192 |
|---|
| 1999 | 631,985 |
|---|
| 2000 | 631,841 |
|---|
| 2001 | 631,758 |
|---|
| 2003 | 631,630 |
|---|
| 2005 | 631,541 |
|---|
| 2006 | 631,456 |
|---|
| 2007 | 631,315 |
|---|
| 2009 | 631,287 |
|---|
| 2011 | 631,253 |
|---|
| 2013 | 631,194 |
|---|
| 2015 | 631,141 |
|---|
| 2017 | 631,113
|
|---|
Trend in threatened rainforest and scrub habitat in the Wet Tropics
| Year | Habitat (hectares)
|
|---|
| 1997 | 1,256,860 |
|---|
| 1999 | 1,256,146 |
|---|
| 2000 | 1,255,652 |
|---|
| 2001 | 1,255,353 |
|---|
| 2003 | 1,255,033 |
|---|
| 2005 | 1,254,679 |
|---|
| 2006 | 1,254,423 |
|---|
| 2007 | 1,254,190 |
|---|
| 2009 | 1,254,070 |
|---|
| 2011 | 1,253,933 |
|---|
| 2013 | 1,253,785 |
|---|
| 2015 | 1,253,527 |
|---|
| 2017 | 1,253,424
|
|---|
Trend in threatened acacia forest, woodland and shrubland habitat in the Wet Tropics
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Trend in threatened wetland and melaleuca open woodland habitat in the Wet Tropics
| Year | Habitat (hectares)
|
|---|
| 1997 | 836,253 |
|---|
| 1999 | 835,044 |
|---|
| 2000 | 834,387 |
|---|
| 2001 | 833,982 |
|---|
| 2003 | 833,587 |
|---|
| 2005 | 833,182 |
|---|
| 2006 | 832,807 |
|---|
| 2007 | 832,308 |
|---|
| 2009 | 832,217 |
|---|
| 2011 | 832,084 |
|---|
| 2013 | 831,914 |
|---|
| 2015 | 831,584 |
|---|
| 2017 | 831,467
|
|---|
Trend in threatened grassland and forbland habitat in the Wet Tropics
| Year | Habitat (hectares)
|
|---|
| 1997 | 0 |
|---|
| 1999 | 0 |
|---|
| 2000 | 0 |
|---|
| 2001 | 0 |
|---|
| 2003 | 0 |
|---|
| 2005 | 0 |
|---|
| 2006 | 0 |
|---|
| 2007 | 0 |
|---|
| 2009 | 0 |
|---|
| 2011 | 0 |
|---|
| 2013 | 0 |
|---|
| 2015 | 0 |
|---|
| 2017 | 0
|
|---|
Trend in threatened heath and other coastal community habitat in the Wet Tropics
| Year | Habitat (hectares)
|
|---|
| 1997 | 118,242 |
|---|
| 1999 | 118,206 |
|---|
| 2000 | 118,158 |
|---|
| 2001 | 118,128 |
|---|
| 2003 | 118,105 |
|---|
| 2005 | 118,095 |
|---|
| 2006 | 118,047 |
|---|
| 2007 | 117,960 |
|---|
| 2009 | 117,956 |
|---|
| 2011 | 117,947 |
|---|
| 2013 | 117,915 |
|---|
| 2015 | 117,897 |
|---|
| 2017 | 117,885
|
|---|
Download data from Queensland Government Open Data Portal
Metadata
Hectares of threatened terrestrial flora habitat predicted to have occurred across Queensland and per bioregion prior to land clearing and remaining as remnant vegetation between 1997 and 2017. Potential habitat has been created using both MAXENT which uses species presence records combined with 7 environmental layers (annual mean temperature, temperature seasonality, annual precipitation, mean moisture index of the lowest quarter moisture index, pre-clearing broad vegetation group, land zone and terrain ruggedness) and buffered species records. Habitat is refined using Regional Ecosystems mapping (version 11, 2019).
