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DARLING RIVERINE PLAINS BIOREGION Background Report

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

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

adspersa) (FSC 2001c).<br />

7.2.2 Potential Threatening Processes<br />

Competition from honeybees (Apis mellifera) (preliminary determination)<br />

The NSW Scientific Committee have made a preliminary determination to list competition<br />

from honeybees as a key threatening process under the TSC Act. Breeding colonies of<br />

honeybees compete with native hollow-dependant fauna for tree hollows. At least 20% of<br />

bird species are hollow dependant (Saunders et al. 1982) and all native arboreal marsupials<br />

depend on tree hollows except the koala (Lindenmayer et al. 1991). Threatened species likely<br />

to be affected by competition from feral honeybees include the squirrel glider, Major<br />

Mitchell’s cockatoo, glossy black-cockatoo and superb parrot (NPWS 2001a).<br />

Honeybees, both feral and managed, often remove up to 80% of the floral resources produced<br />

by plants, and this may result in the displacement of native fauna such as honeyeaters and<br />

native bees which rely on these resources (Paton 1993, 1996, 2000; Sugden & Pyke 1991;<br />

Sugden et al. 1996). Apiary has an unmeasured impact on biodiversity and some studies have<br />

shown that where nectar and pollen resources are limited Apis mellifera may reduce the<br />

degree of seed set in some plant species (Gibbs & Muirhead 1998; Paton 1996; Pyke &<br />

Blazer 1985).<br />

Alteration to the natural flow regimes of rivers and streams and their floodplains and<br />

wetlands (preliminary determination)<br />

The NSW Scientific Committee has made a preliminary determination to list ‘alteration to the<br />

natural flow regimes of rivers and streams and their floodplains and wetlands’ as a key<br />

threatening process under the TSC Act. The NSW Scientific Committee has found that this<br />

process is recognised as a major factor contributing to loss of biological diversity and<br />

ecological function in aquatic ecosystems, including floodplains (NPWS 2001a). The NSW<br />

Scientific Committee describes alterations to natural flow regimes as either reducing or<br />

increasing flows, altering seasonality of flows, reducing frequency, duration and magnitude<br />

of flow events, altering water levels and increasing the rate of fall of water levels (Walker<br />

1985; Cadwallader & Lawrence 1990; Gehrke et al. 1995; Kingsford 1995. Maheshwari et al.<br />

1995; Robertson et al. 1999, 2001; NPWS 2001a).<br />

A high proportion of flow alterations to the majority of streams across New South Wales have<br />

had a major impact on the pattern of natural flows in these waterways. Alteration of flows<br />

reduces habitat by changing the area, frequency and duration of flooding of floodplains and<br />

terminal wetlands. Increasing flows causes more permanent flooding of wetlands, riparian<br />

zone degradation, increased habitat for invasive species, and loss or disruption of ecological<br />

function. Threatened species recorded within the DRP affected by this process include the<br />

blue-billed duck, and freckled duck (NPWS 2001a).<br />

Installation and operation of instream structures that modify flow (proposed<br />

recommendation)<br />

The Fisheries Scientific Committee has made a recommendation to list ‘Installation and<br />

operation of instream structures that modify flow’ as a key threatening process under the<br />

FMA, 1994. The Fisheries Scientific Committee identifies instream structures which modify<br />

flow as including dams, weirs, navigation locks, floodgates, culverts, flow regulators, levee<br />

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