DARLING RIVERINE PLAINS BIOREGION Background Report
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 />
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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