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DARLING RIVERINE PLAINS BIOREGION Background Report

DARLING RIVERINE PLAINS BIOREGION Background Report

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16/08/02 Darling Riverine Plains Bioregion <strong>Background</strong> <strong>Report</strong><br />

3.5 SUMMARY AND PROPOSED FURTHER WORK<br />

3.5.1 Summary<br />

The vegetation of the DRP has been described in a variety of ways and at several levels of<br />

detail. There have been some attempts to describe the pre-European vegetation at both a<br />

landscape level and for smaller portions of the bioregion. However, detailed survey and<br />

mapping has been very limited. Broadscale mapping has mostly been from aerial photo<br />

analysis, which is limited to a crude structural analysis and naming of the dominant tree<br />

species, but this has not been extensively ground truthed. There has also been variation in the<br />

scale of vegetation mapping between the east and the western portions of the bioregion with<br />

smaller quadrat sizes being used in the east.<br />

In broad terms the original vegetation of the DRP is thought to have been open woodland on<br />

alluvial fans and riverine corridors. The height and density of the overstorey decreased from<br />

east to west and the grassy ground cover was dominated by Mitchell grasses (Astrebla<br />

species). Since European settlement the proportion of grassland has increased and is<br />

dominated by introduced species. Description of the pre-European vegetation is of most value<br />

in determining the rate and extent of change that may have occurred as a result of European<br />

settlement of the bioregion. The 1750 mapping by Carnahan (1976) indicates that the lower<br />

reaches of the Darling floodplains within the bioregion were Astrebla grasslands. This region<br />

then suffered from a period of extreme conditions as a result of drought in association with<br />

rabbit infestation and sheep grazing resulting in almost total denudation of the landscape.<br />

This area has now recovered and is dominated by black bluebush communities. Carnahan’s<br />

mapping indicates that there has been a change in the dominant plant community after the<br />

recovery of the landscape or that the area is at a seral stage in the re-establishment of the<br />

vegetation. Any attempts to map pre-European vegetation based on existing remnants should<br />

consider these possibilities and ensure that detailed analyses of historical documents are also<br />

incorporated.<br />

The existing broad vegetation communities within the DRP have been defined by several<br />

authors. These descriptions show a high degree of consistency and fifteen communities can<br />

be described. These include seven forest/woodland communities, tall Acacia shrublands,<br />

saltbush shrublands, grasslands with varying dominant genera (Astrebla, Triodia or<br />

Austrostipa) and wetland, swamp and marsh communities. While these community<br />

definitions are not based on systematic floristic surveys and could be considered subjective,<br />

their consistency indicates that they provide a sound broad definition of the plant<br />

communities of the bioregion. The fundamental importance of riverine and alluvial landforms<br />

is clearly demonstrated by the dominance of water tolerant communities.<br />

Variation within these broad plant communities has not been mapped across the bioregion but<br />

the mapping of land units by Walker (1991) in the Western Region and the relationship<br />

between topographic variation and vegetation associations indicated by Morgan and Terrey<br />

(1990) for all provinces provide an indication and could be analysed further. The more<br />

detailed vegetation descriptions for small areas within the bioregion could be used to verify<br />

these descriptions.<br />

Of the plant communities occurring within the DRP, the Corymbia tessellaris open forest,<br />

Acacia loderi shrublands, and the Artesian Springs community are listed under the TSC Act.<br />

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