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Response to Info Request - Attachment 6a - Ecological Assessment Part 1 MCU18-0015 & RAL18-0015 · MCU18/0015
Ecological Assessment – Attunga Heights
The quality of habitat for reptiles is strongly determined by the structural characteristics
of vegetation (e.g. complexity of vegetation density and vertical strata) and ground cover
(e.g. woody debris and rocky outcrops) which influence micro-climate, solar irradiance and
the availability of suitable basking and shelter sites (Garden et al. 2007). The majority of
leaf litter and ground cover occurs in the lower slopes of the creek line, and therefore the
greatest diversity of reptiles can be expected in this area.
4.3.4 Birds
A total of twenty-one (21) species were recorded during the survey periods (TABLE 7). All
species are listed as ‘common’ under the under the NCWR 2006 and the EPBC Act 1999. No
threatened bird species were recorded.
TABLE 7
BIRD SPECIES RECORDED AT THE STUDY SITE
Scientific Name Common Name Year Recorded
Aegotheles cristatus Owlet nightjar 2003
Alectura lathami Australian brush-turkey 2003, 2018
Cracticus torquatus Grey butcherbird 2003, 2018
Dicrurus bracteatus Spangled drongo 2003, 2018
Eurystomus orientalis Dollarbird 2003
Eudynamys scolopacea Common koel 2003
Manorina melanocephala Noisy miner 2003, 2018
Meliphaga Lewinii Lewin's honeyeater 2003, 2018
Oriolus sagittatus Olive-backed oriole 2003, 2018
Pachycephala pectoralis Golden whistler 2003, 2018
Podargus strigoides Tawny frogmouth 2003, 2018
Sericornis frontalis White-browed scrubwren 2003, 2018
Sphecotheres viridis Figbird 2003, 2018
Strepera graculina Pied currawong 2003, 2018
Zosterops lateralis Silvereye 2003, 2018
Dacelo novaeguineae Laughing kookaburra 2018
Trichoglossus moluccanus Rainbow lorikeet 2018
Anthochaera chrysoptera Little wattlebird 2018
Philemon corniculatus Noisy friarbird 2018
Eopsaltria australis Eastern yellow robin 2018
Colluricincla harmonica Grey shrike-thrush 2018
Searches beneath Allocasuarina species present on the site did not reveal the presence of
any chewed cones, which are indicative of Glossy black cockatoo presence.
The significance of near coastal environments of the New South Wales Far North Coast and
South East Queensland as over-wintering habitat for migratory birds has been established
by many observers and bird banders, including Keast (1968), Robertson (1973), Gravatt
(1974), Porter (1982) and Robertson and Woodall (1983). These patterns may be
attributable to the relatively high winter temperatures and long growing season of this
region compared with the rest of south-eastern Australia (Fitzpatrick and Nix 1973;
Edwards 1979; Nix 1982; Specht et al 1981). Many insectivorous birds from higher latitudes
and elevation over-winter in the locality. These include species such as the Fantail cuckoo
Job No: Q12038/RW3 JWA Pty Ltd 30
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