The Vertebrate Fauna of Jenolan Karst Conservation Reserve: Final
The Vertebrate Fauna of Jenolan Karst Conservation Reserve: Final
The Vertebrate Fauna of Jenolan Karst Conservation Reserve: Final
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8 FURTHER SURVEY AND MONITORING<br />
8.1 LIMITATIONS OF THE CURRENT SURVEY<br />
At the completion <strong>of</strong> the current systematic and targeted surveys, all vertebrate fauna groups (with the<br />
exception <strong>of</strong> frogs) have been systematically sampled to an adequate baseline level for use in<br />
biodiversity assessment. All key habitats within the reserve have also now been adequately sampled.<br />
Groups and individual species that were not adequately sampled are discussed below, followed by<br />
suggested further fauna survey and monitoring programs in sections 8.2 and 8.3. It should be noted<br />
that as the current surveys were undertaken between February and May, it is likely that some<br />
seasonal visitors were not recorded, such as eastern koel. Most <strong>of</strong> these will have been recorded<br />
incidentally via other sources but will be absent from the systematic data. Additionally species that are<br />
cryptic in nature, present in low-densities or restricted to inaccessible habitats, may not have been<br />
recorded or been under recorded.<br />
As mentioned above, the only fauna group not adequately sampled were the frogs. Frogs are best<br />
sampled during humid and/or rainy conditions, preferably during spring and early summer. Conditions<br />
during the current surveys were dry, and surveys were undertaken in late summer and autumn. More<br />
surveys for frogs are required to obtain an accurate assessment <strong>of</strong> what species occupy the reserve.<br />
Individual species that were not adequately targeted include the brush-tailed phascogale, long-nosed<br />
potoroo, red-necked pademelon and bettongs. <strong>The</strong> brush-tailed phascogale was targeted during the<br />
current survey by spotlighting searches along with collection <strong>of</strong> predator scats and hair-tube surveys;<br />
however the best method to survey for this species is through the erection and monitoring <strong>of</strong> artificial<br />
nest boxes (Soderquist et al. 1996). This would represent a study in its own right and was outside the<br />
limitations <strong>of</strong> this program. A proposed survey and monitoring program for this species is a high<br />
priority and is discussed further below in section 8.2.4: further fauna survey – mammals.<br />
Medium-sized terrestrial mammals (especially the long-nosed potoroo, red-necked pademelon, and<br />
bettong species, which appear to have become locally extinct), were targeted during this survey with<br />
camera traps, hair tubes and scat searches. Nonetheless, these species can be cryptic, especially<br />
when they occur in very low densities. Further targeted surveys are required to confirm their absence.<br />
A proposed survey and monitoring program for these species is a high priority and is discussed further<br />
in section 8.<br />
Microbats have now been surveyed to a satisfactory baseline level. However, despite targeting a<br />
considerable proportion <strong>of</strong> time to this group, questions remain. Due to the importance <strong>of</strong> the<br />
subterranean habitat at JKCR, this group remains a priority for further survey and research. In<br />
consideration <strong>of</strong> the complexity and extent <strong>of</strong> the karst system and requirements for access, it was<br />
only possible to inspect a targeted subset <strong>of</strong> caves. While our understanding <strong>of</strong> the key cave-dwelling<br />
species and the key areas used is adequate, an actual evaluation <strong>of</strong> what species occur in every cave<br />
was beyond the limits <strong>of</strong> this survey. Our understanding <strong>of</strong> cave usage by vertebrates throughout the<br />
reserve, particularly our knowledge <strong>of</strong> the more remote and inaccessible caves, will continue to grow if<br />
information gathered by guides and cavers continues to be collated in corporate databases. For more<br />
information on systems for data capture see section 9.6.2: maintaining wildlife data systems for cavedwelling<br />
fauna.<br />
8.2 FURTHER FAUNA SURVEY<br />
<strong>The</strong> systematic and targeted fauna survey work undertaken in JKCR in 2011 has resulted in an<br />
adequate baseline understanding <strong>of</strong> terrestrial vertebrate fauna in the reserve, with the exception <strong>of</strong><br />
amphibians. In addition, the work has highlighted issues that require further study to broaden the<br />
understanding <strong>of</strong> fauna in the locality and region, and enable effective management in the long term.<br />
<strong>The</strong> following surveys are recommended to address these issues. <strong>The</strong> relative priority <strong>of</strong> each<br />
program is given in brackets. In addition to the factors discussed below, any further survey within the<br />
cave system should follow guidelines set out in the Cave Access Policy (DECCW 2010a).<br />
8.2.1 Frogs<br />
Targeted searches for the stuttering frog (suspected species loss) and Booroolong frog (potential<br />
to occur) should be conducted as part <strong>of</strong> a systematic amphibian survey <strong>of</strong> JKCR. Surveys should<br />
also aim to determine the taxonomy <strong>of</strong> some common frogs <strong>of</strong> JKCR that have undergone recent<br />
taxonomic changes i.e. are the resident leaf-green tree frogs Litoria phyllocroa or L. nudidigita?<br />
<strong>The</strong> location and status <strong>of</strong> the Bibron’s toadlet (a regional priority identified in DECC (2007) within<br />
<strong>The</strong> <strong>Vertebrate</strong> <strong>Fauna</strong> <strong>of</strong> <strong>Jenolan</strong> <strong>Karst</strong> <strong>Conservation</strong> <strong>Reserve</strong> 105