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MCU14/0106 & OPW15/0001 Appendix F - Ecological and Bushfire Management Response
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Supplementary Ecological Assessment Report
Noosa Civic Expansion
Table 3-2 Results of Targeted Flora Survey
Scientific Name Common EPBC NC Habitat Likelihood of
Name Status Status occurrence
Allocasuarina Mt Emu She-oak E E The Emu Mountain Sheoak grows Absent (Habitat
emuina in open and closed heath on fine- present is
grained rhyolite rocky slopes (Mt marginal; species
Peregian) and in wallum heath on not recorded
undulating coastal plain. (DoE, during surveys)
2014a)
Eucalyptus Swamp E E The Swamp Stringybark occurs on Absent (Habitat
conglomerata Stringybark coastal flats up to 30m above sea present is
level. It occurs mostly in the marginal; species
ecotone between wet heath not recorded
(wallum) and tall open forest during surveys)
communities. (DoE, 2014b)
Glycine argyrea - - NT Glycine argyrea occurs on sand Absent (Habitat
hills behind the high sand cliffs or present is
behind sand dunes of the marginal; species
immediate sea front, in tall not recorded
Eucalyptus, Acacia and Casuarina during surveys)
woodland with an understory of low
shrubs (Tindale, 1984).
Lobelia - - NT Refer to above text Absent
membranacea
Pararistolochia Richmond - NT The Richmond Richmond Birdwing Absent (Potential
praevenosa Birdwing Butterfly Vine grows in upland habitat is present
Butterfly Vine rainforest and subtropical associated with
rainforest (CANBR, 2010) Covenant J,
however species
not recorded
during surveys)
Allocasuarina emuina, Eucalyptus conglomerate, Glycine argyrea and Pararistolochia praevenosa were not
recorded within the Study Area during the five day flora survey in April and May 2013. These species were
not observed during the one day flora survey on 31 March 2015, supporting original findings that these species
are absent from the survey site. That is, a total survey effort of 12 search days (i.e. two ecologists over six
days) has shown these species to be absent.
3.3 Fauna Management within Open Air Spaces
A number of fauna species have the potential to represent nuisance wildlife in the proposed open air pedestrian
link within Covenant J. Species of potential concern include Brush Turkey, Noisy Miner, Rat species, and the
Australian White Ibis. Impacts from fauna species will be managed through the use of hardscape and
landscape design, and supplemented with additional fauna management controls.
The design of the pedestrian footbridge eliminates potential use by a number of species. The footbridge is a
raised (to a maximum height of ~2m) above ground which eliminates the likelihood of use of the space by
ground dwelling fauna (e.g. reptiles and amphibians). Additionally, the footbridge will abut native vegetation
on either side thus providing a dense habitat structure which is unfavourable to the Australian White Ibis, a
species which in urban areas prefers open spaces such as landfills, constructed wetlands, parks and street
trees (Martin et al. 2011). Design features, such as guards on climbable structures, will be integrated into the
built structure to prevent access by native and exotic rats (Baker et al. 1994).
28 April 2015 Cardno 6
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