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NSW Bitou Bush Threat Abatement Plan - Department of ...

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38<br />

<strong>Threat</strong> <strong>Abatement</strong> <strong>Plan</strong> - Invasion <strong>of</strong> native plant communities by Chrysanthemoides monilifera<br />

Committee in its determination <strong>of</strong> bitou bush as a KTP (<strong>NSW</strong> SC 1999a). The determination<br />

identified three threatened fauna species potentially at risk from bitou bush, namely the eastern<br />

bristlebird (Dasyornis brachypterus), little tern (Sterna albifrons) and beach stone-curlew (Esacus<br />

neglectus).<br />

Anecdotal and observational evidence suggests that bitou bush invasion can result in the decline<br />

<strong>of</strong> some native bird populations, for example those that nest or roost in hind-dunes such as little<br />

terns (S. albifrons: Ross pers. comm.). In addition, monthly counts <strong>of</strong> shorebirds on Pelican<br />

Island, <strong>of</strong>f Port Macquarie showed that as bitou bush and lantana increased on the island, bird<br />

densities declined (NPWS 2002a). The contribution <strong>of</strong> bitou bush and lantana to this decline,<br />

while suspected, is unknown. The effects <strong>of</strong> bitou bush invasion on bird communities are not<br />

consistent across bird species. On the South Coast, canopy-feeding generalists and understorey<br />

insectivores were found to be more abundant in some bitou bush infested areas than some areas <strong>of</strong><br />

native vegetation (French and Zubovic 1997).<br />

The sprawling branches, dense foliage cover, long flowering period and abundant fleshy fruit<br />

production <strong>of</strong> bitou bush may provide shelter and food for some animals (French and Eardley<br />

1997). However, simply because bitou bush <strong>of</strong>fers a potential food resource does not mean that<br />

animals utilise or prefer this resource to their typical diet. The presence <strong>of</strong> bitou bush did not<br />

appear to affect fruit removal rates by birds for co-occurring native shrub species (Gosper et al.<br />

2005). <strong>Bitou</strong> bush may only be a minor food resource for birds, as fruits are only present for a<br />

short period <strong>of</strong> the year, however during fruiting, this temporary food source may be exploited by<br />

generalist feeders, rather than specialists as highlighted by the list <strong>of</strong> species reported to consume<br />

bitou bush fruits (Dodkin and Gilmore 1984 and Table 5.1).<br />

Not all bird species that consume bitou bush fruits are effective dispersers (e.g. crimson rosella<br />

(Platycercus elegans)), and for many other birds effective dispersal is only assumed (e.g. from the<br />

occurrence <strong>of</strong> bitou bush plants beneath emergent trees/perching sites). European red foxes<br />

(Vulpes vulpes) consume high quantities <strong>of</strong> bitou bush fruits and are effective dispersers <strong>of</strong> its<br />

seeds (Meek 1998). Unlike many native coastal plants, bitou bush flowers in winter and provides<br />

an important food source for many animals during late winter/early spring (French and Eardley<br />

1997). Conversely, the reduction in native species that flower in summer due to bitou bush<br />

infestation may result in a food shortage for many animals such as specialist frugivores,<br />

nectarivores and insectivores (Dodkin and Gilmore 1984). Twenty-three bird species and three<br />

mammal species have been reported to feed on bitou bush (Table 5.1).<br />

French and Zubovic (1997) recommend further study to elucidate the responses <strong>of</strong> individual bird<br />

species to bitou bush invasions. Of particular concern is the role <strong>of</strong> coastal habitats in providing<br />

sources <strong>of</strong> nectar for fauna over winter, a period <strong>of</strong> regional shortage, following bitou bush<br />

invasion and competition (Dodkin and Gilmore 1984; Law et al. 2000; Gosper 2004b). Similar<br />

studies for mammals are also needed, especially given that the only mammal species for which<br />

there is information are introduced ones, and nectar/pollen feeding bats (see Table 5.1).<br />

Subsequent to the release <strong>of</strong> the draft TAP (see DEC 2004), information has been compiled on<br />

fauna species which may be at risk from bitou bush invasion (Table 5.2). Unfortunately, most <strong>of</strong><br />

this information was not available prior to completion <strong>of</strong> this plan and thus no assessments have<br />

been made <strong>of</strong> the exact nature <strong>of</strong> the threat or how the impacts due to bitou bush invasion might<br />

be reduced or sites where control will be beneficial. In addition, it appears that the WINS<br />

assessment tool (see Downey in press) may also be useful in determining fauna at risk, based on

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