Indicator: LD-01 The proportion and area of native vegetation and changes over time
Data
Prior to European settlement native vegetation covered most of Australia but now only 87% of the country is vegetated by native species. Most of the change has been from clearing of forests and woodlands, which originally covered 54% of the country and now covers 42% of the country. The following table provides a more detailed analysis of native vegetation remaining.
While grasslands, which were the most extensive original vegetation, have not been extensively modified, their condition is largely unknown.
Native forests and woodlands have born the brunt of the clearing. Since European settlement, about a quarter of Australia’s native forests and woodland has been cleared, mainly in what is now the intensive land use zone.
The following table shows the Native Vegetation Inventory Assessment (NVIS) of native vegetation by type prior to European settlement and as at 2001-2004.
| Vegetation type | Pre settlement | NVIS 2005 | Difference | Percentage lost | Percentage left | Percentage of remaining vegetation in reserves |
|---|---|---|---|---|---|---|
| Rainforest and vine thickets | 53,469 | 35,200 | 18269 | 34% | 66% | 54% |
| Eucalyptus Tall Open Forest | 40,801 | 35,344 | 5457 | 13% | 87% | 34% |
| Eucalyptus Open Forest | 394,280 | 272,121 | 122159 | 31% | 69% | 23% |
| Eucalyptus Low Open Forest | 4,726 | 3,952 | 774 | 16% | 84% | 35% |
| Eucalyptus Woodland | 1,362,263 | 892,920 | 469343 | 34% | 66% | 8% |
| Acacia Forest and Woodlands | 495,059 | 408,632 | 86427 | 17% | 83% | 9% |
| Callitris Forest and Woodlands | 40,278 | 32,296 | 7982 | 20% | 80% | 6% |
| Casuarina Forest and Woodland | 166,303 | 149,262 | 17041 | 10% | 90% | 19% |
| Melaleuca Forest and Woodland | 106,057 | 99,561 | 6496 | 6% | 94% | 10% |
| Other Forests and Woodlands | 80,772 | 72,414 | 8358 | 10% | 90% | 10% |
| Eucalyptus Open Woodland | 498,663 | 458,905 | 39758 | 8% | 92% | 6% |
| Tropical Eucalyptus woodlands/grasslands | 115,503 | 112,481 | 3022 | 3% | 97% | 13% |
| Acacia Open Woodland | 320,981 | 314,040 | 6941 | 2% | 98% | 8% |
| Mallee Woodland and Shrubland | 387,230 | 271,529 | 115701 | 30% | 70% | 37% |
| Low Closed Forest and Tall Closed Shrublands | 25,819 | 16,278 | 9541 | 37% | 63% | 31% |
| Mangroves | 9,664 | 9,325 | 339 | 3% | 97% | 33% |
| Total forest and woodland | 4,101,868 | 3,184,260 | 917,608 | 22% | 78% | |
| Acacia Shrubland | 865,845 | 851,274 | 14571 | 2% | 98% | 10% |
| Other Shrublands | 157,530 | 123,464 | 34066 | 22% | 78% | 19% |
| Chenopod Shrub, Samphire Shrub and Forbland | 447,239 | 436,801 | 10,438 | 2% | 98% | 13% |
| Total shrublands | 1,470,614 | 1,411,539 | 59,075 | 4% | 96% | |
| Heath | 9,256 | 8,071 | 1,185 | 13% | 87% | 44% |
| Tussock Grassland | 559,850 | 525,888 | 33,962 | 6% | 94% | 3% |
| Hummock Grassland | 1,368,861 | 1,367,973 | 888 | 0% | 100% | 10% |
| Other Grassland, Herbland, Sedgeland and Rushland | 67,977 | 64,810 | 3,167 | 5% | 95% | 17% |
| Total grassland | 1,996,688 | 1,958,671 | 38,017 | 2% | 98% | |
| Total native vegetation | 7,578,427 | 6,562,541 | 1,015,885 | 13% | 87% | 54% |
| Woody native veg cleared since settlement | 4,092,204 | 3,174,935 | 917,269 | 22% | 78% | |
| Other veg cleared since settlement | 3,476,558 | 3,378,281 | 98,277 | 3% | 97% |
The following figure shows these data graphically and also shows the proportion of each broad type of vegetation that is to some degree protected by virtue of being in reserves.
Areas of estimated pre-1750 and remaining (2001-04) vegetation in Australia (km2); area of remaining vegetation in reserves
The following maps show the change spatially. The whited out areas on the 2001-2004 map are the 13 per cent of Australia that has lost its native vegetation cover.
Estimated Pre-1750 Vegetation in Australia: Major Vegetation Groups
Present (2001-2004) Vegetation in Australia: Major Vegetation Groups
The following map shows IBRA regions by the percentage of total native vegetation remaining in each of them.
Percentage of vegetation remaining by IBRA regions
Source: Department of the Environment and Heritage 2005, National Vegetation Information System (NVIS) Stage 1, Version 3.0 Major Vegetation Groups, viewed N/A, http://www.deh.gov.au/erin/nvis/mvg/index.html
Source: Parks Australia 2006, National Reserve System Programme Priority Review (in prep.), DEH, Canberra.
The following map shows the number of vegetation groups with less than 30% remaining by IBRA regions.
Vegetation groups with 30% remaining by IBRA region
Source: Department of the Environment and Heritage 2005, National Vegetation Information System (NVIS) Stage 1, Version 3.0 Major Vegetation Groups, viewed N/A, http://www.deh.gov.au/erin/nvis/mvg/index.html
Source: Parks Australia 2006, National Reserve System Programme Priority Review (in prep.), DEH, Canberra.
Source: Department of the Environment and Heritage 2006, National Vegetation Information System (NVIS) Stage 1, Version 3.0 Major Vegetation Groups, viewed 30 May 2006, http://www.deh.gov.au/erin/nvis/mvg/index.html
Source: Department of the Environment and Heritage 2006, National Reserve System Programme Priority Review 2006 (in prep.), DEH, Canberra.
For further information about the NVIS data see:
What the data mean
About 87% of Australia’s pre-European vegetation remains although clearing has not been uniform across major vegetation types. Many vegetation types have undergone significant changes since European arrival. ‘Low closed forest and tall closed shrublands’, for example, was uncommon and now is even more so, with only 63% remaining. About 66% of ‘rainforest and vine thickets’, remains. The rarest pre-European vegetation type was ‘Eucalyptus low open forest’ - about 84% remains. The most widespread pre-European vegetation type was hummock grasslands (covering about 18% of Australia) and most of it still remains although its condition and density of hummocks may have decreased due to grazing, weeds and other pressures. It is the densely settled coastal, temperate regions (originally mainly native forest and woodland), particularly on the eastern coast of the continent, that have lost most of their vegetation. Of the 13% of Australia’s original vegetation that has been lost since European settlement, most has been forests and woodlands. Almost a quarter of Australia’s native forests and woodland has been cleared, mainly in what is now the intensive land use zone.
However, the AGO data derived from remote sensing (see LD-03 Change in extent and proportion of woody vegetation, clearing and regrowth ) suggest that the situation may be even worse. According to these data, woody vegetation covers only 33% of the area estimated to be under woody native vegetation by NVIS, with only 26% of the continent’s original area of woody vegetation remaining.
Data Limitations
Methodologies for deriving quantitative assessments of the status of Australia’s native vegetation have been further developed since the native vegetation assessment undertaken for the National Land and Water Resources Audit in 2001, making comparisons between the NVIS estimates in 2005 and the Audit estimates in 2001 difficult.
The data does not indicate condition of the vegetation.
Methodologies for deriving quantitative assessments of the status of Australia’s native vegetation vary considerably.
The following table shows the NLWRA 2001 assessment of pre-European vegetation (by major vegetation type) and the more recent NVIS assessment of pre-European vegetation, with the Audit’s 2001 assessment of current vegetation and the NVIS 2005 assessment of current vegetation. The table shows the difficulty showing recent vegetation trends while methodologies for data collection and data interpretation continue to improve.
| Pre-European (NLWRA 2001 assessment) |
Pre-European (NVIS 2005 assessment) | NLWRA 2001 assessment (Data date 1997) |
NVIS 2005 (Data date 2001-2004 excl. NSW 1997-2004) |
|
|---|---|---|---|---|
| Forest and woodland (inc. some associated shrub, heath and grassland) | 3 724 754 | 4 092 204 | 2 878 795 | 3 174 935 |
| Other shrub and heath | 1 397 105 | 1 480 675 | 1 331 481 | 1 419 610 |
| Hummock grass | 1 756 962 | 1 368 861 | 1 756 104 | 1 367 973 |
| Tussock grass | 589 212 | 559 850 | 528 998 | 525 888 |
| Other grassland | 100 504 | 67 977 | 98 523 | 64 810 |
| Other (inc. bare ground, water bodies, mangroves, etc) | 112 063 | 106 999 | ||
| Cleared/modified | Nil | Nil | 982 051 |
Source: Department of the Environment and Heritage 2005, National Vegetation Information System (NVIS) Stage 1, Version 3.0 Major Vegetation Groups, viewed N/A, http://www.deh.gov.au/erin/nvis/mvg/index.html
Source: National Land and Water Resources Audit 2001, Fragmentation of Australia's Native Vegetation: Applications, Australian Native Vegetation Assessment 2001, viewed 5 Jun 2006, http://audit.deh.gov.au/ANRA/vegetation/docs
/Native_vegetation/nat_veg_applications.cfm
Issues for which this is an indicator and why
Land — Land condition - Condition of terrestrial species and ecological communities
To fully understand what is happening to species, habitats and ecological communities, we would need indicators that show long term changes in number of species present within each habitat and habitat type, changes in numbers and distribution within each species, both within each habitat and between different habitats, an understanding of how each different species interacts with each other species and of seasonal, climatic and anthropogenic changes in habitats. To understand these processes at a continental scale, we would need to have this information across all habitats comprising the continent’s ecosystems.
Even if these interactions were understood, we would need sufficient historical data or understanding of ecological processes to know whether a major fluctuation between species is indicative of a natural, ecologically beneficial process or is a symptom of anthropogenic degradation.
No indicators, which either individually or collectively have the capacity to do this, have been identified. In the absence of any way of assessing the overall condition of all aspects of Australia’s terrestrial biodiversity, and the ecosystem as a whole, considering the condition of a selection of key species, communities and habitats is probably the best we can do. Known declines in species, communities or habitats may be indicative of broader declines in species communities and habitats. In particular, the extent of native vegetation which provides habitat for species may serve as a surrogate indicator for the general condition of the species and ecological communities which maintain the overall condition of the land.
Vegetation provides habitat for life forms from all the kingdoms (other plants, animals, fungi, bacteria and viruses). While the mere presence (extent) of vegetation is not necessarily indicative of the condition of either the vegetation itself or of the other things that live there, the ecological communities which maintain the overall condition of the land are more likely to still be present where native vegetation is still present. Therefore, the extent of native vegetation may serve as a surrogate indicator for the general condition of the species, habitats and ecological communities which maintain the overall condition of the land.
Other indicators for this issue:
- LD-03 Change in extent and proportion of woody vegetation, clearing and regrowth
- LD-17 Fragmentation of remnant vegetation
- BD-02 Conservation status of nationally significant species and ecological communities, compared with previous years
Land — Land condition - Land cover
Extent of woody vegetation is a key indicator of the condition of land cover. Woody vegetation is predominantly perennial and generally contributes to deeper and more stable surface soil, deeper root systems and groundwater, better protection for surface water, a more life-friendly microclimate and a more secure habitat for other plants and animals. It therefore contributes to the capacity of the land to maintain its vegetative cover. Extent and change in extent of native vegetative cover is a direct indicator for this issue.
Other indicators for this issue:
- LD-03 Change in extent and proportion of woody vegetation, clearing and regrowth
- LD-17 Fragmentation of remnant vegetation
Land — Direct pressure of human activities on the land - Land clearing
While all the original vegetation cleared in Australia was, by definition, native vegetation, it is the perennial, deep-rooted, woody vegetation which is most significant in terms of providing habitats for other biota and protecting soil, micro-climate and water catchments. It is this type of vegetation that has seen the most significant reductions since the European invasion. Extent and change in vegetative cover show the extent of these reductions.
Other indicators for this issue:
- LD-03 Change in extent and proportion of woody vegetation, clearing and regrowth
- LD-17 Fragmentation of remnant vegetation
- LD-20 Total grazing pressure relative to net primary productivity
- BD-13 Examples of the impact of grazing on biodiversity
Land — Direct pressure of human activities on the land - Species introduction and species change
Change in extent of native species is also an indicator for change in extent of introduced (non-native) vegetation species. It may also be a surrogate indicator for distribution of naturalised fauna because naturalised fauna tend to be better adapted than native fauna to introduced vegetation.
Other indicators for this issue:
- LD-19 Land use and land use change
- LD-40 Current research into pressures and contributions of naturalised introduced species
- LD-20 Total grazing pressure relative to net primary productivity
- LD-35 Temporal and spatial correlation between changing fire regimes and species change
- BD-12 Examples of the impacts of fires on biodiversity
- BD-13 Examples of the impact of grazing on biodiversity
- IW-37 Examples of carp pressures and measures for removal and/or commercial catch
- IW-38 Cane toad distribution
- IW-39 Examples of significant wetland weeds
- BD-09 The change in extent of selected nationally significant invasive species
- BD-10 Examples of native species whose populations have declined where various invasive species have established resident populations
Biodiversity — Landscapes - Ecosystem diversity
It is reasonable to assume that landscapes which retain their original vegetation cover with a minimum of modification, are likely to retain a higher proportion of their original biodiversity than landscapes that have been highly modified. The extent of native vegetation types compared with that existing prior to European settlement indicates the broad range of terrestrial habitats lost and remaining. The indicator can help identify vegetation types at risk from pressures such as increases in the extent of dryland salinity.
Other indicators for this issue:
Biodiversity — Pressures on biodiversity - Land clearing
Clearing of native vegetation removes the biodiversity living there both directly and by removing its habitat. Extent of land cleared of native vegetation gives a broad indication of the extent to which biodiversity has been affected.
Other indicators for this issue:
- LD-17 Fragmentation of remnant vegetation
- BD-08 Estimated loss of biodiversity resulting from land clearing
Biodiversity — Species, habitats and ecological communities - Conservation status of species and ecological communities
Extent of native vegetation of various types remaining is indicative of the conservation status of those vegetation types.
Other indicators for this issue:
- BD-02 Conservation status of nationally significant species and ecological communities, compared with previous years
- BD-04 Listed threatened species or ecological communities for which recovery action is showing stable or increasing populations
- IW-30 Macroinvertebrate condition
- IW-31 Fish - Abundance and distribution
- IW-32 Frogs - Abundance and distribution
- IW-33 Abundance and distribution of waterbirds
- CO-01 Trends in selected groups of coastal and marine species and habitats
- CO-02 Number of marine species that are endangered or threatened and changes in population/ distribution of selected threatened species
- CO-16 Status of Australian fisheries
- AAT-08 Plankton populations
- AAT-09 Seabird populations
- AAT-10 seal populations
- AAT-11 Whale populations
- AAT-12 Changes in colonies of plants on Heard Island
Inland Waters — Catchment scale influences — Land and vegetation condition - Vegetation
Native vegetation is a determinant of the condition of inland waters. Vegetation helps keep the water table low and protects surface waters by shading them from direct sunlight and holding banks together. Native vegetation cleared is an indicator for this pressure on inland waters.
Other indicators for this issue:
- IW-26 Forested streamlength
- IW-34 Examples of deterioration of condition of wetland vegetation
- LD-03 Change in extent and proportion of woody vegetation, clearing and regrowth
- LD-17 Fragmentation of remnant vegetation
Further Information
Extensive additional analysis of vegetation data are available in the source document and also in the NHT publication “Landscape Health in Australia”. The source of the data used in these reports in the National Vegetation Inventory System.
- Australian Native Vegetation Assessment 2001
- Australia's State of the Forests Report 2003
- News from the Department of Agriculture and Food, Western Australia
- The Australian Natural Resources Atlas
Changes to this document since December 2006
The first table reported against the indicator was missing its first column and included old data that had been updated prior to publication of SoE 2006. Some text had also been omitted from the section entitled "What the data mean", and some source information was also missing. These errors and omissions have been corrected.
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