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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 />

provide habitat for benthic plants;<br />

lead to organic enrichment by capturing detritus and contributing to secondary production<br />

by degradation of the debris itself;<br />

provide refuges from predators and interactions between competitors for fish and<br />

invertebrates;<br />

provide velocity refuges that minimise energy costs of swimming;<br />

provide spawning sites essential for successful reproduction;<br />

provide home range markers for territorial and migratory fish species;<br />

provide refuge and spawning habitats in the riparian zone during overbank flooding;<br />

assist in erosion prevention by stabilising sediments of stream banks and riparian zones;<br />

and<br />

assist in the scouring of deep holes adjacent to woody debris which acts as temperature<br />

and drought refuges.<br />

Threatened fish species that occur within the DRP and which are affected by this process<br />

include trout cod (Maccullochella macquariensis) and silver perch (Bidyanus bidyanus) (FSC<br />

2001a).<br />

Degradation of native riparian vegetation along New South Wales water courses<br />

‘Degradation of native riparian vegetation along New South Wales water courses’ has been<br />

listed as a key threatening process under the FMA 1994. The Fisheries Scientific Committee<br />

defines riparian vegetation as “any vegetation on land which adjoins, directly influences, or is<br />

influenced by a body of water” (FSC 2001b). Degradation of native riparian vegetation<br />

includes invasion of riparian vegetation by non-native species. Negative effects of<br />

degradation of native riparian vegetation include increased amounts of sediment and nutrients<br />

via runoff and increased light penetration to the waterbody leading to increased algal growth<br />

and smothering of benthic communities, reduced inputs of organic carbon which are a major<br />

energy source in most stream ecosystems, reduced inputs of large woody debris entering the<br />

system leading to a reduction in spawning and habitat sites of several fish and aquatic<br />

invertebrates, destabilisation of river banks, and reduced overhanging riparian vegetation<br />

leading to decreased shelter and shade for fish. Threatened fish species recorded within the<br />

DRP affected by this process include trout cod (Maccullochella macquariensis), Murray<br />

hardyhead (Craterocephalus fluviatilis), and silver perch (Bidyanus bidyanus) and the<br />

endangered populations of purple-spotted gudgeon (Mogurnda adspersa), and olive perchlet<br />

(Ambassis agassizii) (FSC 2001b).<br />

Introduction of fish to fresh waters within a river catchment outside their natural range<br />

‘Introduction of fish to fresh waters within a river catchment outside their natural range’ is<br />

listed as a key threatening process under the FMA, 1994. Introduced fish recorded in the DRP<br />

(brown trout (Salmo trutta), rainbow trout (Onchorynchus mykiss), European carp (Cyprinus<br />

carpio), goldfish (Carassius auratus), gambusia (Gambusia holbrooki) and redfin perch<br />

(Perca fluviatilis)) all have self-sustaining populations within the waterways of New South<br />

Wales (FSC 2001c). Introduced fish affect populations of native fauna and flora by direct<br />

predation, competition for food, competition for spawning localities, competition for habitat,<br />

habitat degradation through uprooting vegetation and disturbance of sediments and promotion<br />

of the spread of diseases in native species. Threatened fish species recorded within the DRP<br />

affected by this process include Murray hardyhead (Craterocephalus fluviatilis), trout cod<br />

(Maccullochella macquariensis), and silver perch (Bidyanus bidyanus) the endangered<br />

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