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Byron Flora and Fauna Study 1999 - Byron Shire Council

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BYRON FLORA AND FAUNA STUDY, <strong>1999</strong><br />

Appendix 9<br />

A call survey of bats of <strong>Byron</strong> <strong>Shire</strong>, NSW<br />

H Parnaby, PO Box 2359, Coffs Harbour 2450<br />

September 1998.<br />

Report prepared for L<strong>and</strong>mark Ecological Services.<br />

INTRODUCTION<br />

A survey of bats was undertaken at 52 sites within <strong>Byron</strong> <strong>Shire</strong> during the period 6 April - 7 May, 1998. The<br />

survey relied primarily on detection of calls using the Anabat call detection system, <strong>and</strong> was designed to<br />

target species considered to be of particular conservation concern, <strong>and</strong>/or that were known from few<br />

records from the region. The survey targeted a subset of those listed as Vulnerable on Schedule 2 of the<br />

NSW Threatened Species Conservation Act, 1995 <strong>and</strong> are listed in Table 1.<br />

Table 1 Priority species targeted during the survey<br />

First priority species<br />

Yellow-bellied Sheathtail-bat<br />

Beccari’s Freetail-bat<br />

Eastern Freetail-bat<br />

Second priority species<br />

Golden-tipped Bat<br />

Eastern False Pipistrelle<br />

Eastern Tube-nosed Bat<br />

Hoary Wattled Bat<br />

Eastern Cave Bat<br />

Large-eared Pied Bat<br />

SURVEY METHODS<br />

Surveys were undertaken using h<strong>and</strong> held bat detectors, <strong>and</strong> calls analysed using the Anabat5 call detection<br />

system <strong>and</strong> software (Titley Electronics, Ballina). The duration of surveys per site varied from 10 to 60<br />

minutes, depending on levels of activity. Manually operated surveys were used rather than automated recording<br />

methods, as the operator was able to track the bat <strong>and</strong> thereby obtain better quality call sequences of longer<br />

duration, thereby increasing the ability to obtain species identifications from calls.<br />

Bat species recognition is not always possible from echolocation calls. Some call sequences are too distant<br />

or indistinct, or too brief to enable species identification. The variation in call types exhibited by some<br />

species is still not properly defined <strong>and</strong> calls of some species are very similar <strong>and</strong> cannot be reliably<br />

distinguished for some species. Consequently, three categories of confidence in species identification are<br />

recognised (Parnaby 1992):<br />

Definite identification (X): species identity not in doubt;<br />

Probable identification (P): species identification most likely, but a low probability of confusion<br />

with species with similar call types;<br />

Possible identification (): call characteristics are comparable with the species, but a reasonable<br />

probability of confusion with one or more similar species.<br />

Call surveys were made at a total of 52 sites. Sites less than about 100 m apart were designated as subsites,<br />

unless significantly different habitat was sampled. Some sites were resampled, <strong>and</strong> the total number of<br />

censuses was 63, for a total duration of approximately 30 hours. Site location, date, start time <strong>and</strong> duration<br />

of surveys at each site are given in Table 3.<br />

197

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