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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 />

6 OTHER FAUNA<br />

6.1 INVERTEBRATES<br />

Very little is known about invertebrate diversity within the bioregion. Not only is this<br />

knowledge of importance for assessing the biodiversity of the area, but invertebrates also<br />

perform an essential role in ecosystem function. They are of critical importance as food for<br />

many species (such as bats, insectivorous birds, water birds, waders, dasyurids and reptiles)<br />

and play an important role as decomposer organisms and in nutrient cycling. Some species<br />

can also be agricultural pests. Due to the lack of information about invertebrates, it is not<br />

possible to estimate rates of extinction or decline. As invertebrates play a critical role in the<br />

functioning of natural systems, improving the information base and therefore the conservation<br />

management for this group is critical to any strategy for conserving biodiversity (New 1984;<br />

NPWS 1992). A list of invertebrate taxa recorded from the DRP is shown in Appendix G.<br />

6.1.1 Aquatic invertebrates<br />

Rivers and streams exist as a patchwork of habitats, which can be classified into three broad<br />

habitat types for aquatic invertebrates. Macrohabitats are the large distinct reaches of the river<br />

system; mesohabitats are smaller habitats including the main channel, backwaters, billabongs,<br />

effluent creeks and floodplain channels; and microhabitats are the smallest habitat types<br />

which include snags (fallen timber), aquatic vegetation and different substrate types.<br />

In a survey of aquatic invertebrates in these three primary habitat types in the Darling River<br />

between Bourke and Wilcannia, Sheldon (1995) found insects were the dominant group,<br />

comprising 85% of taxa and 81% of individuals. Of these Dipterans (flies) and Coleopterons<br />

(beetles) were most abundant. Billabongs had a greater number of taxa and individuals than<br />

channel habitats and temporary billabongs had more individuals than permanent billabongs.<br />

Overall, river geomorphology was found to significantly influence aquatic invertebrate<br />

assemblages through the diversity of mesohabitats and microhabitats it supports. Flow<br />

regulation also modifies the assemblage composition by favouring the development of<br />

specific microhabitat and isolating mesohabitats (Sheldon 1995).<br />

In the Macquarie Marshes a baseline survey of aquatic invertebrates found 197 taxa of which<br />

85% were insects (65 Coleopteron taxa, 54 Dipterans, 24 Hemipterans). In general, cumbungi<br />

swamps, lagoons, slow moving streams and intermittent streams had the greatest number of<br />

taxa present (Bray 1994a). Cherax destructor (yabby), a common resident in the Marshes,<br />

survives dry periods by burrowing into the mud.<br />

112

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