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Appendix D Terrestrial and Aquatic Biodiversity - Environment ...

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SZ247: Bat survey from the Western Desert Resources Towns River project area, NT<br />

main report, as determined by EcOz <strong>Environment</strong>al. Nets were attended at all times for<br />

between 3 – 5 hours after the end of civil twilight. In addition, a harp trap was left for two full<br />

nights in thick riparian vegetation surrounding a small creek flowing from a rocky outcrop<br />

(Corymbia polycarpa Mid Open Woodl<strong>and</strong>; site H01; 1 – 2/2/2012).<br />

Captured bats were given a field identification based on their appearance <strong>and</strong> by noting<br />

distinguishing characters described by Churchill (2008). A wing biopsy was taken for genetic<br />

analysis (see section 3.7 below), <strong>and</strong> the individuals were released within 2 hours at the<br />

capture site. Only one individual was euthanised (using 0.1 mL Nembutal; under the South<br />

Australian Museum's 'Licence to possess an S4 drug', licence number 2011-76256): the<br />

single specimen of Saccolaimus captured at M03 on 3/2/2012.<br />

3.6 Searches for roosts<br />

Two types of bat roost were considered during the survey: caves <strong>and</strong> crevices in rocky<br />

outcrops; hollows <strong>and</strong> beneath the bark of trees. The use of a helicopter to access water<br />

bores across the MLA – Towns River project area during the survey period provided an<br />

excellent opportunity to check the entire lease for rocky outcrop <strong>and</strong> make a determination of<br />

whether those formations observed could provide underground habitat suitable for bats<br />

(transect HEL01; Figure 2). The vegetation communities across the project area were also<br />

observed from the helicopter in order to define patches that had the largest hollow-forming<br />

tree species (typically Eucalyptus tretrodonta <strong>and</strong> E. miniata).<br />

Three relatively brief (c. 1-hour long) searches were made in Eucalyptus woodl<strong>and</strong> habitats<br />

for roosts of S. saccolaimus using a novel method based on video observation. A small<br />

video camera <strong>and</strong> white LED light source was attached to the end of a 10 m telescopic carbon<br />

fishing rod <strong>and</strong> either lowered down into vertical hollows (1 – 2 m) or poked into horizontal<br />

hollows. The video feed was recorded onto a small digital recorder for later examination. A<br />

variety of hollows were targeted, particularly those large enough to contain bats of medium<br />

size (i.e. Saccolaimus spp.) such as deep vertical hollows in the main trunk. Usage of this<br />

type of hollow has been noted previously, for example a recent discovery of a colony in Cairns<br />

(G. Ford pers. comm. 27/1/2012). While it has been used by other bat researchers in<br />

Australia previously (e.g. Reardon 2000), the pole camera is not a st<strong>and</strong>ard piece of<br />

equipment for surveying bats as part of environmental assessments in Australia, <strong>and</strong> it was<br />

essentially being evaluated for its utility on the present survey.<br />

3.7 Identification from DNA barcoding<br />

The identity of captured bats was to be confirmed through DNA barcoding, given that the area<br />

has not been surveyed well for bats previously, <strong>and</strong> to provide a more robust basis for species<br />

name allocation compared to a simple morphological examination in the field. A tissue<br />

biopsy was taken from the wing membrane of each capture using a sterile 4 mm dermal<br />

punch, <strong>and</strong> stored in 50:50 saline:ethanol solution.<br />

In the laboratory, the biopsies were first soaked for 24 hours in phosphate buffered saline<br />

solution to remove the ethanol, <strong>and</strong> then extracted with a Gentra DNA purification kit. Two<br />

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