THE REPTILE FAUNA OF THE UPPER BILLABONG CREEK CATCHMENT AREA, SOUTHERN NEW SOUTH WALES

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HERPETOFAUNA TEXT 38-1 1/7/08 3:01 PM Page 41 THE REPTILE FAUNA OF THE UPPER BILLABONG CREEK CATCHMENT AREA, SOUTHERN NEW SOUTH WALES Steven Sass 1,2, David M. Watson 2 and Andrea Wilson 2 1 nghenvironmental, PO Box 470, Bega, NSW 2550. Email: steven@nghenvironmental.com.au. 2 Ecology and Biodiversity Group, Institute for Land, Water and Society, Charles Sturt University, Thurgoona, NSW 2640. ABSTRACT The Upper Billabong Creek Catchment Area is centred on the rural town of Holbrook in southern New South Wales. The catchment has undergone significant changes over the past 120 years resulting in widespread clearing of native vegetation. Despite comprehensive research on birds, mammals and vascular plants throughout the region, the reptile fauna has received little attention in surveys within this fragmented landscape. Systematic surveys for reptiles in 2005-06 recorded 28 species and revealed differences in reptile distribution patterns across the catchment. A review of previous studies and records from the NSW Atlas of Wildlife database provide an additional 12 species, giving a total of 40 species known to be present in the Upper Billabong Creek Catchment. The presence of reptiles of conservation significance is discussed, including the recent detection of the Pink-tailed Worm Lizard (Aprasia parapulchella). This species is listed as endangered under both NSW and Commonwealth legislation and it is recommended that catchment-wide surveys to better understand their distribution be given high priority. This paper provides a comprehensive inventory of reptile fauna in the Upper Billabong Creek Catchment for natural resource managers. INTRODUCTION The Upper Billabong Creek catchment area in southern New South Wales has undergone extensive clearing, much of which occurred some 120 years ago (Woodward, 1998). As a result, remaining native vegetation comprises many small fragments accounting for less than 10% of its original extent (Woodward, 1998). Many of these fragments are classified as grassy box woodland (also referred to as box gum woodland), an endangered ecological community recognised under Schedule 3 of the NSW Threatened Species Conservation Act 1995 and also the Commonwealth Environment Protection and Biodiversity Act 1999. In recent years, several workers have provided general information on the status and distribution of herpetofauna across the wider south-west slopes region (Annable, 1995; Daly, 2004; Lemckert, 1998; Michael, 2004; Sass, 2003). Despite the ecological importance of the Upper Billabong Creek catchment community, few studies have specifically focussed on the reptile fauna within the area. However, with the upgrading of the Hume Highway to dual carriageway within this catchment, several environmental assessments have been undertaken during the past 12 months. To better understand the reptile fauna of the Upper Billabong Creek catchment area and make informed decisions about their future management, a comprehensive inventory of these species is an important tool for natural resource managers. This paper documents the reptile fauna of the Upper Billabong Creek area recorded during a study undertaken in 2005/06 (see Sass, 2007) and reviews previous studies available in the scientific literature to develop a comprehensive inventory of reptile species for the catchment. Herpetofauna 38 (1) 2008 Page 41

HERPETOFAUNA TEXT 38-1 1/7/08 3:01 PM Page 42 Figure 1. Location of the Upper Billabong Creek Catchment study area. Page 42 Herpetofauna 38 (1) 2008

HERPETOFAUNA TEXT 38-1 1/7/08 3:01 PM Page 43 Study area METHODS The study area is located within the Upper Billabong Creek catchment in southern NSW (Figure 1). The catchment is around 80,000 hectares in area (Baker et al., 2001) and is located within the South Western Slopes Bioregion (Thackway & Creswell, 1995) bordered by the Riverina bioregion to the west and the South Eastern Highlands bioregion to the east. The study area occupies a transitional climatic region between the more mesic highland areas to the east and the drier plains to the west (Caughley & Gall, 1985). The mean annual rainfall is approximately 700 mm, however, this varies widely across the catchment with up to 900 mm in the far south-east to 550 mm in the west of the catchment (Bureau of Meterology, 2006; Caughley & Gall, 1985). Vegetation types The vegetation types within the Upper Billabong Creek catchment reflect the changing geology and climate of the region (Table 1). Dry foothill forests dominate the upper slopes and ridges of the east, while grassy box woodlands favour the lower slopes and rises in the central and western parts of the catchment (Costello, 2001). River red gum (Eucalyptus camaldulensis) dominates the riparian areas and floodplains, however, in the east, Blakely s red gum (E. blakelyi) occupies most riparian areas (Costello, 2001). Elevation The Upper Billabong Creek catchment has a wide elevation range which is likely to influence vegetation communities and faunal assemblages of the study area. The highest parts of the catchment occur in the upper slopes and ridges of the east peaking at 889 metres above sea level (asl), while the plains in the west are as low as 220 m asl (CSIRO, 2002). Survey methods Between September 2005 and January 2006 reptiles were surveyed across 43 sites which included 40 fragments ranging from 1 ha to 28 ha and three larger reference sites (between 115 ha and 2500 ha) using pitfall traps with drift fences over 1,144 pitfall trap nights and active hand searches for 92 person hours. Further details of survey methods are detailed in Sass (2007). Searches of the DECC NSW Atlas of Wildlife database, Internet sites, journal paper data- Table 1. A general description of the vegetation types within the study area Vegetation type Dry foothill forest Grassy box woodland Riverine forest/woodland General description A medium forest up to 15 m tall which is usually dominated by Red Stringybark Eucalyptus macrorhyncha. Other species of eucalypt that are co-dominant included inland Scribbly Gum E.rossi, Apple Box E. bridgesiana and Bundy E.nortonii. An open woodland community where the dominant overstorey species are White Box Eucalyptus albens, Yellow Box E. melliodora and/or Blakely's Red Gum E. blakelyi. An open forest or woodland of up to 25 m tall dominated by River Red Gum E. camaldulensis that occurs on alluvial soils along watercourses in the west of the catchment, whilst Blakely s Red Gum E.blakelyi replaces this species in the east. Herpetofauna 38 (1) 2008 Page 43

HERPETOFAUNA TEXT 38-1 1/7/08 3:01 PM Page 44 bases and consultations with researchers who have worked in the study area were undertaken to identify previous studies that included reptile surveys. Nomenclature in this paper follows Swan et al. (2004) except for Lerista muelleri and Crytoblepharus carnabyi. Lerista muelleri has recently been revised, and the species in New South Wales is now Lerista rhodonoides (Smith & Adams, 2007). Similarly, Cryptopblepharus carnabyi has also undergone revision, and the species in south-eastern New South Wales is now Cryptoblepharus pannosus (Horner, 2007). Where no common name is provided, nomenclature follows the NSW Atlas of Wildlife database (DECC, 2007). This study RESULTS Systematic surveys of the 43 study sites identified a total of 28 reptile species across the Upper Billabong Creek Catchment during this study (Table 2). Four species of reptile were recorded in the study area for the first time: Egernia saxatilis intermedia, Egernia whitii, Pseudemoia entrecasteauxii and Tiliqua nigrolutea (Sass et al., 2007). These species are typically associated with cool climates and moderate to high altitude areas in New South Wales (DECC, 2007; Swan et al., 2004). Only one individual of each of these species was recorded suggesting they occur in low densities. Some reptile species were found only on the eastern side of the study area such as the small skinks, Ctenotus taeniolatus, Hemiergis decresiensis talbingoensis, Lampropholis delicata and the small dragon Amphibolurus muricatus. Conversely, some reptile species were found exclusively in the western or central portions of the study area such as the small skinks, Ctenotus robustus, Cryptoblepharus pannosus and Lampropholis guichenoti. Additionally, several species pairs within several genera were found to occupy separate areas of the study area with some overlap in the centre of the study area in the genus Ctenotus (Sass, 2007). Other studies A review of previous research or surveys conducted in the Upper Billabong Creek catchment revealed a total of seven technical reports and manuscripts that have included reptiles in their field surveys. Herring (2003) covered much of the study area in a survey of birds, mammals and reptiles as part of a catchment-wide biodiversity study. His study revealed 22 reptile species, many exhibiting commonality to this study with the exception of Lerista bougainvillii, Menetia greyii and Parasuta dwyeri (Herring, 2003). Three environmental assessment reports for proposed developments in the study area provide no additional reptile species other than previously recorded species (Klomp & Fairbridge, 1992; Klomp et al., 1995; Klomp & Marshall, 1995). In more recent times, two technical reports have included reptile surveys as part of a larger environmental assessments for the upgrade of the Hume Highway to dual carriageway through the catchment (Parsons Brinkerhoff, 2007; SKM, 2006). These surveys identified two additional species to previous studies. The Pink-tailed Worm-lizard (Aprasia parapulchella) and Ctenotus orientalis were recorded between Yarra Creek and Holbrook (Parsons Brinkerhoff, 2007). Both surveys were confined to a narrow lineal strip that, in most parts, was adjacent to the existing highway. DECC NSW Atlas of Wildlife Database Searches of the NSW Atlas of Wildlife database for the study area identified an additional seven species not recorded in this study or in previous studies. These species were the dragon, Amphibolurus nobbi, four species of skinks (Acritoscincus platynotus, Egernia cunninghami, Eulamprus heatwolei, Eulamprus tympanum), one species of snake (Ramphotyphlops proximus)and one species of pygopod (Lialis burtonis) (DECC, 2007). Page 44 Herpetofauna 38 (1) 2008

HERPETOFAUNA TEXT 38-1 1/7/08 3:01 PM Page 45 Table 2. Reptile species recorded in the Upper Billabong Creek Catchment Area (x = recorded, SWW = this study, PB = Parsons Brinkerhoff 2007, SKM = Sinclair Knight Mertz 2007, HER = Herring 2003, DECC = NSW Atlas of Wildlife Database Scientific Name Common Name SWW PB HER SKM DECC Gekkonidae Christinus marmoratus Marbled Gecko x x x Diplodactylus vittatus Eastern Stone Gecko x x x Strophurus intermedius Southern Spiny-tailed Gecko x Pygopodidae Aprasia parapulchella Pink-tailed Worm-lizard x Delma inornata Plain Snake-lizard x x x Lialis burtonis Burtons Legless Lizard x Varanidae Varanus gouldii Sand Goanna x Varanus varius Lace Monitor x x Agamidae Amphibolurus muricatus Jacky Lizard x x x Amphibolurus nobbi Nobby Dragon x Pogona barbata Eastern Bearded Dragon x x Scincidae Acritoscincus platynotus Red-throated Skink x Carlia tetradactyla Southern Rainbow Skink x x x Cryptoblepharus pannosus Carnaby's Wall Lizard x x x Ctenotus orientalis Eastern Striped Skink x Ctenotus robustus Robust Ctenotus x x x Ctenotus taeniolatus Copper-tailed Skink x x x Egernia cunninghami Cunningham's Skink x Egernia saxatilis intermedia Black Rock Skink x Egernia striolata Tree Skink x x Egernia whitii White's Skink x Eulamprus heatwolei Yellow-bellied Water Skink x Eulamprus tympanum Southern Water Skink x Hemiergis decresiensis talbingoensis Three-toed Earless Skink x x x Lampropholis delicata Garden Sun-skink x Lampropholis guichenoti Grass Sun-skink x x x Lerista bougainvillii Southern Lerista x x x Lerista rhodonoides Three-toed Lerista x Menetia greyii Grey's Skink x Morethia boulengeri Boulenger's Morethia x x x Pseudemoia entrecasteauxii Woodland Tussock Skink x Tiliqua nigrolutea Blotched Blue-tongue x Tiliqua scincoides Eastern Blue-tongue x x x Typhlopidae Ramphotyphlops nigrescens Blackish Blind Snake x x Ramphotyphlops proximus Woodland Blind Snake x Pythonidae Morelia spilota metcalfei Carpet Python (Murray Darling form) x x Elapidae Parasuta dwyeri Dwyer's Black headed Snake x x Pseudechis porphyriacus Red-bellied Black Snake x x x Cheluidae Chelodina longicollis Long-necked Turtle x x Herpetofauna 38 (1) 2008 Page 45

HERPETOFAUNA TEXT 38-1 1/7/08 3:01 PM Page 46 Table 3. Reptile fauna recorded during this study and their distribution across the study area. (WESTERN = Only at sites on western side of Hume Highway, EASTERN = Only at sites on eastern side of Hume Highway, BOTH = At sites on both sides of Hume Highway, * = Recorded). Scientific Name Common Name WESTERN EASTERN BOTH Gekkonidae Christinus marmoratus Marbled Gecko * Diplodactylus vittatus Eastern Stone Gecko * Strophurus intermedius Southern Spiny-tailed Gecko * Pygopodidae Delma inornata Plain Snake-lizard * Varanidae Varanus gouldii Sand Goanna * Varanus varius Lace Monitor * Agamidae Amphibolurus muricatus Jacky Lizard * Pogona barbata Eastern Bearded Dragon * Scincidae Carlia tetradactyla Southern Rainbow Skink * Cryptoblepharus pannosus Carnaby's Wall Lizard * Ctenotus robustus Robust Ctenotus * Ctenotus taeniolatus Copper-tailed Skink * Egernia saxatilis intermedia Black Rock Skink * Egernia striolata Tree Skink * Egernia whitii White's Skink * Hemiergis decresiensis talbingoensis Three-toed Earless Skink * Lampropholis delicata Garden Sun-skink * Lampropholis guichenoti Grass Sun-skink * Lerista rhodonoides Three-toed Lerista * Morethia boulengeri Boulenger's Morethia * Pseudemoia entrecasteauxii Woodland Tussock Skink * Tiliqua nigrolutea Blotched Blue-tongue * Tiliqua scincoides Eastern Blue-tongue * Typhlopidae Ramphotyphlops nigrescens Blackish Blind Snake * Pythonidae Morelia spilota metcalfei Carpet Python (Murray Darling form) * Elapidae Pseudechis porphyriacus Red-bellied Black Snake * Cheluidae Chelodina longicollis Long-necked Turtle * Page 46 Herpetofauna 38 (1) 2008

HERPETOFAUNA TEXT 38-1 1/7/08 3:01 PM Page 47 DISCUSSION An important part of natural resource management is to improve our understanding of biodiversity across catchments and landscapes (eg, Sass et al., 2005; Sass & Wilson, 2006). This study provides important information to natural resource managers on the distribution of reptiles across the Upper Billabong Creek catchment with a total of 28 species being recorded. A review of previous studies and database records increases the total number of reptile species for the study area to 40 (Table 2). A number of species exhibited notable geographic trends in their distribution across the catchment (Table 3). The concept of faunal subregions within Australia has been widely discussed and is generally upheld to explain patterns of reptile distribution varying only slightly between families (Cogger & Heatwole, 1981). The south-west slopes bioregion, of which the study area is a part, is regarded as the natural boundary between species classified as Bassian and Eyrean (Caughley & Gall, 1985). The transitional zone between these classifications has not yet been identified, however, it could be said that the Hume Highway is situated in such a zone. This is due to the rise in elevation to the mountains on the eastern side of the route, while the western side of the highway generally has little topographic relief. Two species pairs of skinks show complementary patterns in their occurrence: Ctenotus taeniolatus and C. robustus, and Lampropholis delicata and L. guichenoti. Ctenotus robustus is considered widespread, while C. taeniolatus is regarded as Bassian (Caughley & Gall 1985). Similarly, both species of Lampropholis are regarded as Bassian (Caughley & Gall 1985). The species pairs in Ctenotus and Lampropholis were only recorded in sympatry at one study site. The causes of this pattern of distribution require further investigation. Amphibolurus muricatus, Egernia saxatilis intermedia, Egernia whitii, Hemiergis decresiensis talbingoensis, Pseudemoia entrecasteauxii and Tiliqua nigrolutea were only found on the eastern side of the Hume Highway, whereas Cryptoblepharus carnabyi, Lerista rhodonoides and Varanus gouldii were only found on the western side of the Hume Highway. These results suggest that the corridor of the Hume Highway within the Upper Billabong Creek catchment may coincide with the transition between Eyrean and Bassian faunal subregions. Similar patterns of distribution were also found in a recent study near Tumut (north-east of the study area) and were suggested to be influenced by contact between species inhabiting the Bassian and Eyrean fauna subregions (Fischer et al., 2005). Two species of conservation significance have been recorded in the study area: the Murray- Darling form of the Carpet Python (Morelia spilota metcalfei) and the Pink-tailed Wormlizard (Aprasia parapulchella). One other species of conservation significance, the Striped Legless Lizard (Delma impar), has not been recorded in the Upper Billabong Creek Catchment area. but is also expected to occur in the study area given a recent record of its occurrence near Tarcutta (40 km to the north of the study area) (Ecology Partners, 2007; SKM, 2006). Suitable areas of habitat in the form of extensive areas of rock outcropping occur in the catchment and the species' absence is likely to be an artefact of its cryptic nature and difficulty in surveying. One individual Murray-Darling form of the Carpet Python was recorded in the north of the study area near the township of Cookardinia (Sass, 2007). Although not listed as a threatened species under NSW or Commonwealth legislation, this species has long been regarded as being under threat in fragmented landscapes (Heard et al., 2004; Damian Michael, pers. comm. 2007). The 12.36 ha woodland fragment from which this species was recorded had good quantities of fallen timber, numerous hollow bearing trees and small areas of rock outcropping, all of which meet the thermal and shelter needs for this species (Heard et al. 2004). The Yellow- Herpetofauna 38 (1) 2008 Page 47

HERPETOFAUNA TEXT 38-1 1/7/08 3:01 PM Page 48 footed Antechinus (Antechinus flavipes) was frequently recorded in the pitfall traps during the survey, and also noted as present by other researchers working at the site (Terry Korodaj and Matt Herring, pers. comm., 2007), and is likely to provide a valuable food resource for this python species. Five individual Pink-tailed Worm-lizards were found amongst granite outcrops east of the highway corridor below Morgan s Ridge (Parsons Brinkerhoff, 2007). This species is listed as endangered under the NSW Threatened Species Conservation Act 1995 and the Commonwealth Environment Protection and Biodiversity Conservation Act 1999. Searches of a small number of rock outcrops across the study area (Sass, 2007) and by the senior author at Little Billabong for the proposed duplication of the Hume Highway (SKM, 2006) failed to detect this species despite extensive searches. The Pink-tailed Worm-lizard has been recorded from similar granite outcrops near Albury in the south (Michael & Herring, 2005) and Tarcutta in the north (Jones, 2004). Weather and environmental conditions play an important role in detecting this species (Osborne & Jones, 1995), and the effectiveness of previous surveys for this species may have been limited by these factors. Considering their presence at other similar outcrops in adjacent catchments, it is possible that this threatened species occurs at other sites in the Upper Billabong Creek Catchment. Catchment-wide targeted surveys for this species are required to gain a greater understanding of its distribution across the catchment. ACKNOWLEDGMENTS We are indebted to the many landholders in the Upper Billabong Creek catchment for allowing access to their special 'blocks of bush'. Thanks to Simon McDonald of the CSU Spatial Analysis Network (SPAN) for map production. An Australian Research Council grant (DMW) and Royal Zoological Society of NSW Ethel Mary Read grant (SS) provided funding for this research. Matt Herring provided valuable technical support and encouragement along the way. We also thank the two reviewers for their comments and to Glenn Shea for updates on taxonomic revisions relevant to this manuscript. All sampling was carried out under Scientific Research Permit S10921 issued by the Department of Environment and Climate Change (Parks and Wildlife Division) and the authority of Charles Sturt University Animal Care and Ethics Committee approval 05/054. A special thanks to all the volunteers who assisted in pitfall trap installation and sampling, especially Linda Sass, Frances Cory and Daniel Reppion. REFERENCES Bureau of Meterology 2006. www.bom.gov.au. [Accessed 2006]. Annable, T.J. 1995. Annotated checklist of the reptiles of Wagga Wagga and district, NSW. Herpetofauna 25(1): 22-27. Baker, P., Please, P., Coram, J., Dawes, W., Bond, W., Stauffacher, M., Gilfedder, M., Probert, M., Huth, N., Gaydon, D., Keating, B., Moore, A., Simpson, R., Salmon, L. & Stefanski, A. 2001. Assessment of Salinity Management Options for Upper Billabong Creek catchment, NSW: Groundwater and Farming Systems Water Balance Modelling. National Land and Resources Audit, Bureau of Rural Sciences, Canberra. Caughley, J. & Gall, B. 1985. Relevance of zoogeographical transition to conservation of fauna : amphibians and reptiles in the southwestern slopes of New South Wales. Australian Zoologist 21: 513-529. Cogger, H.G. & Heatwole, H. 1981. The Australian reptiles: origins, biogeography, distribution patterns and island evolution. Pp. 1331-1373 in, Keast, A. (ed.). Ecological Biogeography of Australia. W. Junk, The Hague. Costello, D. 2001. Holbrook Shire roadside survey & management guidelines. Holbrook Shire Council. Page 48 Herpetofauna 38 (1) 2008

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