In addition, proponents and land managers should refer to the Recovery Plan (where available) or the Conservation Advice (where available) for recovery, mitigation and conservation information.
|EPBC Act Listing Status||Listed as Vulnerable|
|Recovery Plan Decision||
Recovery Plan required, this species had a recovery plan in force at the time the legislation provided for the Minister to decide whether or not to have a recovery plan (19/2/2007).
|Adopted/Made Recovery Plans||
National Recovery Plan for the Striped Legless Lizard (Delma impar): 1999-2003 (Smith, W.J.S. & P. Robertson, 1999) [Recovery Plan].
|Other EPBC Act Plans||
Threat Abatement Plan for predation by feral cats (Department of the Environment, Water, Heritage and the Arts (DEWHA), 2008zzp) [Threat Abatement Plan].
Threat Abatement Plan for Predation by the European Red Fox (Department of the Environment, Water, Heritage and the Arts (DEWHA), 2008zzq) [Threat Abatement Plan].
|Policy Statements and Guidelines||
Referral guidelines for the striped legless lizard, Delma impar (Department of Sustainability, Environment, Water, Population and Communities (DSEWPaC), 2011f) [Admin Guideline].
Survey guidelines for Australia's threatened reptiles. EPBC Act survey guidelines 6.6 (Department of Sustainability, Environment, Water, Population and Communities (DSEWPaC), 2011m) [Admin Guideline].
Federal Register of
Declaration under s178, s181, and s183 of the Environment Protection and Biodiversity Conservation Act 1999 - List of threatened species, List of threatened ecological communities and List of threatening processes (Commonwealth of Australia, 2000) [Legislative Instrument].
Documents and Websites
|State Listing Status||
|Non-statutory Listing Status||
|Scientific name||Delma impar |
This is an indicative distribution map of the present distribution of the species based on best available knowledge. See map caveat for more information.
The Striped Legless Lizard is a well-defined species within a well-defined genus containing 17 species (Cogger 1992).
The Striped Legless Lizard is a member of the family Pygopodidae, the legless or flap-footed lizards (Cogger 1992). As with other members of the legless lizard family, Striped Legless Lizards lack forelimbs and have only very reduced hind limbs. These hind limbs are apparent only as small flaps on either side of the vent. Superficially, these animals resemble snakes, but can be readily distinguished from the latter by the presence of external ear openings, a fleshy undivided tongue and a tail which is longer than the body (Cogger 1992). Striped Legless Lizards can be readily distinguished from other legless lizards by body colouration, body size and head scalation.
The Striped Legless Lizard is a pale-grey lizard up to 30 cm in length, with a maximum snout-vent length (SVL) of about 12 cm. Striped Legless Lizards have a long thin body and the tail, when unbroken, is about twice the length of the body. They have a series of stripes on their sides and the sides of their back, becoming diagonal bands on the tail (Cogger 1992; Wilson & Knowles 1988). These stripes are dark-brown or blackish and extend the whole length of the individual from the neck to the tail. Each stripe has individual black-centered scales. However, in some individuals, particularly juveniles, these stripes may be very faint or absent. The head is generally darker than the body, tending to black in juveniles. The underside of Striped Legless Lizards is whitish and they have a blunt snout (Cogger 2000). The sexes of Striped Legless Lizards appear very similar externally. However, adult males may be distinguished by the presence of a small rounded 'spur' under each hind limb flap (M.A. Rauhala 1998, pers. comm.).
There is significant variation in the size of Striped Legless Lizards in different populations in Victoria. A study at Dashwood found the modal size class to be 6.06.9 g, while a study at Derrimut Grassland Reserve reported the modal size class to be 3.04.1 g (Coulson 1990; Kutt 1992). The modal size class of Striped Legless Lizards captured at the Keilor Plains site was 6.06.9 g. Some generations (size classes) appeared to be uncommon, suggesting that recruitment may be low in some years (O'Shea 1996). Observations of captive animals suggest that Striped Legless Lizards may skip reproduction when not in prime condition (J. Birkett n.d., pers. comm., cited in O'Shea 1996).
The Striped Legless Lizard was formerly distributed throughout temperate lowland grasslands in the Australian Capital Territory (ACT), the south-western slopes and southern tablelands of New South Wales (NSW), central and southern Victoria, and the south-eastern corner of South Australia (SA) (Cogger et al. 1993). The distribution of the species has declined, with many known sites no longer supporting populations (Smith & Robertson 1999). Due to habitat fragmentation the remaining populations are probably small and isolated (Webster et al. 2003).
In NSW, the species occurs at sites near Goulburn, Yass, Queanbeyan, Cooma and Tumut areas (Coulson 1995; NSW DECC 2005am). The formerly continuous distribution in the ACT has been reduced to four discrete areas: Gungahlin, the lower Majura Valley (including the suburb of Lawson), the lower Jerrabomberra Valley and Yarramundi Reach (Coulson 1995; Dorrough 1995; McElhinney 2002). The population at Yarramundi Reach may have become extinct (ACT Government 2005a).
The range of the Striped Legless Lizard in Victoria appears to have contracted to the southern part of the state (Cogger et al. 1993), with extant populations known from the outer western and northern suburbs of Melbourne, near Cressy in the western district, Derrimut Grasslands Reserve, Dashwood (Cogger et al. 1993; Coulson 1995; Webster et al. 2003; Smith & Robertson 1999; Whitby 1995), Merton, Alexandra, Molesworth and Yea (Anon. 2002a). The species was recently recorded on the new section of the Calder Highway from Kyneton to Ravenswood (Victoria). The species is no longer found in the inner metropolitan areas of Melbourne (Cogger et al. 1993).
The species was believed to be extinct in SA in 1993 (Cogger et al. 1993). However populations have been discovered in recent years at Lake Omerod and Hack's Lagoon Conservation Park, near Naracoorte (S. Milne 2001a, pers. comm.). An additional sighting on Kyby-Jesse Road in this area may have indicated an additional population. However, this site has since been destroyed (Milne 1999).
Extent of occurrence
The extent of occurrence of the Striped Legless Lizard is approximately 81 870 km², an area reaching from western SA, through southern Victoria and up through to the ACT and Goulburn in southern NSW. The Striped Legless Lizard is thought to have once extended further into SA (Cogger et al. 1993), thus its extent of occurrence has declined.
Area of occupancy
The total area of occupancy of the Striped Legless Lizard is unknown. However, there is some information on the density of the populations giving an indication of the area of occupancy. For example, the total population is spread across approximately ninety populations (Dorrough & Ash 1999; O'Shea 2005) and occurs in variable density across its range with estimates ranging from 10–40 individuals per hectare (ARAZPA 1996). One of the largest populations in Victoria occurs on the Keilor plains at St Albans, west of Melbourne. Distribution of individuals across this site was not random, with small communities forming within the available habitat (O'Shea 1996). Thus the area of occupancy for this species is likely to be influenced significantly by habitat suitability within its range, and is likely to be significantly less than the extent of occurrence.
Historically, the species has been recorded from 125 sites, of which at least 40 are estimated to still hold populations (ACT Government 1997g; Hadden 1995).
In 1999, a captive group of this species was being held at the Melbourne Zoo in Victoria. This group originated mostly from salvage operations performed prior to destruction of grassland sites for development. Another captive colony was proposed for the Animal House at Victoria University of Technology (Werribee), based on animals salvaged from the Albion grasslands (C. Hocking n.d., pers. comm., cited in Smith & Robertson 1999).
Captive breeding of Striped Legless Lizards was achieved at Melbourne Zoo in 1998, with three young successfully raised from captive matings (Banks et al. 1999). Additional eggs laid in captivity by wild-caught gravid females have been hatched and the juveniles raised (C. Banks et al. n.d., pers. comm., cited in Smith & Robertson 1999; Kukolic 1994). The Royal Melbourne Zoo is releasing Striped Legless Lizards back into the wild in the Organ Pipes National Park (Anon. 2002a).
Extensive surveys have been conducted in the ACT and Victoria, with surveys having been conducted in the ACT annually between 1989 and 1997 (ACT Government 1997g). In Victoria, survey efforts have concentrated in the Melbourne region and some areas in the west of the state. Broad surveys have been conducted in South Australia, which have not located the species (J. Foulkes n.d., pers. comm., cited in Smith & Robertson 1999). Additionally, a few targeted surveys have been conducted in NSW (Smith & Robertson 1999).
There are few population size estimates available for this species. Dorrough and Ash (1999) reported that less than 1000 individuals had been recorded from 90 sites in 1995, however more recent studies indicate that the population may be larger. A study of the species at Iramoo Wildlife Reserve near Melbourne has estimated the average population size to be approximately 600 which is considered to be an underestimate (O'Shea 2005). Thus the total number of individuals of this species is unknown, but likely to be in excess of 1000 individuals.
A population at Dashwood (Victoria) was estimated to consist of 220 individuals in 1995 (Whitby 1995). The population density at a site on the Keilor Plains at St. Albans, west of Melbourne, was approximately 10 Striped Legless Lizards per hectare in 1996, with a total of 68 individuals captured. Densities of between 1040 per hectare were estimated, also in 1996, at a site near Ravenhall (ARAZPA 1996). Of the seven sites currently known to support the species in NSW, two are on private land, one on private rural-residential land, one on council-owned land, two on land managed by the Rural Lands Protection Board (RLPB), and one on land owned by the NSW DECCW. The sites in Victoria outside reserves are on a variety of government and private land, including many rural properties. The sites outside the Gunghalin Reserve in the ACT are on a mix of private leasehold, military, ACT government and Commonwealth government land (Smith & Robertson 1999).
Populations with large numbers of individuals are known from Iramoo Wildlife Reserve, near Melbourne, with at least 600 individuals (O'Shea 2005), Dashwood (Victoria) which was estimated to have 220 individuals (Whitby 1995), and the Keilor Plains, west of Melbourne (O'Shea 1996). These populations are considered important for the species' long-term survival and recovery.
Striped Legless Lizards occur within four reserves in Victoria; Derrimut Grassland Reserve, Iramoo Wildlife Reserve, Terrick-Terrick National Park (north of Bendigo) and Craigieburn Grasslands (north of Melbourne). In the ACT there are three separate, but abutting areas as part of the Gungahlin Grassland Reserve. In NSW, there is the Kuma Nature Reserve, near Cooma; and in SA there is the Lagoon Conservation Park (O'Shea 2005; Parks Victoria 2004a; S. Milne 2001a, pers. comm.; Smith & Robertson 1999). These reserves cover more than 800 ha, e.g. Derrimut Grassland Reserve has an area of 150 ha, the Gungahlin Grassland Reserve covers an area of 500 ha and the Kuma Nature Reserve encompasses an area of 180 ha (O'Shea 2005; Parks Victoria 2004a; S. Milne 2001a, pers. comm.; Smith & Robertson 1999).
Striped Legless Lizards may use refuges within or adjoining their habitat when a fire goes through. For example, after fire this species may move into unburnt areas or remain relatively inactive in the soil or under rocks until the vegetation is able to recover enough to provide shelter (Smith & Robertson 1999).
The life span of the Striped Legless Lizard is estimated to be at least 10 years (Smith & Robertson 1999), with the age at first reproduction thought to be 23 years for males and 34 years for females (Smith & Robertson 1999). Their mating system is not clear and the Striped Legless Lizard is assumed to be polygynous, where males mate with more than one female in a single breeding season (Coulson 1990).
Typically, females lay two eggs in December and January and hatching occurs in January and February, 3560 days after laying (Coulson 1995; Smith & Robertson 1999). It is believed most adult females are capable of breeding every year. There has been one recorded case of communal nesting, with six eggs found in a single nest (Coulson 1995). During November and December, adults are more active than at any other time of the year. This activity is thought to be related to mating and egg-laying requiring increased movements of both sexes (Kutt 1992).
Studies of the diet of the Striped Legless Lizard indicate that this species feeds primarily on spiders, crickets, grasshoppers, Lepidopteran larvae and cockroaches (Coulson 1990; Nunan 1995; Wainer 1992). Lepidopteran larvae appear to be particularly important in the diet of this species, and may play a role in limiting lizard abundance at some sites (Nunan 1995). The foraging mode of this species may alter according to prey types, indicating that Striped Legless Lizards use both ambush and active searching methods (Coulson 1995). However, active searching for prey on the surface is likely to be the predominant mode of foraging (Nunan 1995).
During winter months Striped Legless Lizards enter a state of torpor, although the exact timing and the torpor sites are mostly unknown (Smith & Robertson 1999). It has been found that animals in Victoria overwinter mostly in soil cracks, under/beside rocks and in tussock bases. In the ACT, however, it is assumed that grass tussocks provide the primary overwinter refuges. Activity peaks in spring and summer, particularly in November and December (Coulson 1995). During this period, the majority of foraging occurs during daylight hours (Coulson 1995; Webster et al. 2003).
Little is known about the habits and pattern of movements of this species, although some information has been gained from recapture data and from fluoro-dye tracking (Kukolic 1994; Kutt 1992; Rauhala 1996). Individuals have been recorded moving at least 20 m in one day (Kutt 1992), and up to 50 m over several weeks (K. Kukolic n.d., pers. comm., cited in Smith & Robertson 1999.). This implies that these animals may be relatively wide-ranging, supporting the belief that they are active hunters, at least some of the time (Nunan 1995). Most of the movement records are from the November and December high activity period, and may be due to reproductive activity rather than normal home range movements (Kutt 1992).
Striped Legless Lizards at the Keilor Plains site appeared to have small home ranges, with four of six recaptures occurring less than 10 m from the original capture site (O'Shea 1996).
Surveys for the Striped Legless Lizard can be problematic due to the cryptic nature of the species, as it may not be detected even when present at the site. Recapture rates of those individuals that have been caught are extremely low, but whether the low rate of recapture is a consequence of animal behaviour, inadequate trapping or marking, or a combination of all these factors is unknown (Smith & Robertson 1999), which in turn makes determining life history traits difficult and inhibits adequate survey planning.
Tracking of this species is also problematic and the Victorian Striped Legless Lizard Working Group trialled a harmonic radar diode in the related species D. inornata, but the technique was unsuccessful. Trials of microwave transponders and radioactive isotopes were to be conducted (Smith & Robertson 1999). Other techniques used to monitor this species include thread spool and fluorescent powder tracking (Kutt 1992) and trials were proposed in the recovery plan for heat branding and PIT tags. Freeze branding was shown to be unsuccessful at Tidbinbilla Nature Reserve (Smith & Robertson 1999).
The guidelines below provide a guide for surveys aimed at determining the presence or absence of Striped Legless Lizards at a site. Once detected, survey effort should be adjusted appropriately to determine the relative distribution of the species on the site(s).
Surveys for the Striped Legless Lizard should be conducted from areas of relatively undisturbed native grasslands (including similar habitat connected or immediately adjacent to the site) with a dense cover of perennial tussock grasses, particularly Spear Grass (Stipa bigeniculata); Kangaroo Grass (Themeda triandra); Wallaby Grass (Austrodanthonia spp.); and tussock grasses (Poa spp.). It is also important to note that Striped Legless Lizards can occur in modified grassland areas dominated by weed species such as Chilean Needlegrass (Nassella neesiana); Toowoomba Canary-grass (Phalaris aquatica); and Cocksfoot (Dactylis glomerata) and hence such areas may need to be surveyed.
A three-step survey protocol, outlined below, is recommended.
1. Desktop review
A search of relevant literature and Commonwealth and state/territory databases and maps will provide an indication of whether the species has been previously recorded on a particular site and the overall likelihood of the species occurring in the area.
2. Habitat assessments
Desktop and field assessments of the habitat on the site may provide further indication of the likely presence (or absence) of the species at a site by providing information on whether the site supports known or potentially suitable habitat for the species, distance to the nearest known site supporting the species and/or suitable habitat, and habitat connectivity within the site and to other areas surrounding the site.
3. Targeted field survey
Field surveys for the species should be undertaken during the active period of the species (between September and May). Some survey techniques (such as active searching) may be undertaken during the cooler months of the year, but often with less success. Surveys should target suitable habitat within the site. Reference sites may need to be monitored during the expected active period of the species and used to guide survey timing at the target site(s).
If the species is detected during a survey, all potentially suitable habitat at the site should be considered occupied by the species. All presence/absence data should be provided to a central repository (state environment agencies).
In areas with surface rock, artificial shelter site surveys or active searching should be the primary technique. In areas with little to no rocky habitat (such as the ACT), artificial shelter site surveys or pitfall trapping should be used in conjunction with hand searches around tussocks.
Rock turning can be detrimental to Striped Legless Lizard populations, especially when undertaken regularly. Therefore, this method should be used only when other methods are unavailable and it should never be employed for long-term monitoring.
Survey methods and effort for the Striped Legless Lizard
|Artificial shelter site surveys (for example roof tiles)
The extent of natural temperate grassland, including those known to support the striped legless lizard, has declined severely across Australia (Carter et al. 2003). The loss and degradation of native grassland, through a variety of processes, is the main threat to the survival of the Striped Legless Lizard. Other potentially threatening processes include inappropriate burning regimes and feral animals (Smith & Robertson 1999).
Approximately 99.5% of natural temperate grassland in south-eastern Australia has been destroyed or drastically altered since European settlement (Carter et al. 2003). Threats such as clearance for agricultural and urban development, rock removal, inappropriate fire regimes, habitat fragmentation and weed invasion by Serrated Tussock (Nassella trichotoma), Chilean Needle Grass (N. neesiana) and related species continue to diminish the quantity and quality of this species' habitat (Cogger et al. 1993; Coulson 1995; Webster et al. 2003). Heavy habitat modification by extended intense grazing, pasture improvement, ploughing, and drought can eliminate this species from a site, however, recolonisation and recovery may be possible if the threat is short-term, not too intense and there is undisturbed refuge habitat nearby (Smith & Robertson 1999).
The creation of barriers to lizard movements such as the construction of buildings, roads, and fences can cause populations to become fragmented and isolated from each other. The loss or degradation of habitat can also have the effect of limiting dispersal between patches. Ploughed, overgrazed and bare ground, such as roads or paths, might represent a barrier to dispersal of Striped Legless Lizards and may fragment habitats (Dorrough & Ash 1999).
At the Commonwealth Defence Land, Lawson (ACT), survey results indicate a decline in population that is compounded when grassland is grazed. The change in cover is likely to reduce refuge opportunities for Striped Legless Lizards and their potential prey. Habitat loss also occurs due to increased urban development and fire in the grasslands. It is observed that the present populations at this location may increase as the habitat quality improves (McElhinney 2002).
Fire can be detrimental to this species in two ways: it may increase the risk of predation of this species and its prey (due to loss of cover); or it may cause death directly (Smith & Robertson 1999). Cogger and colleagues (1993) recorded mortality following cool fires in grassland reserves, but the extent to which fire is a threat to populations is unknown (Smith & Robertson 1999). The behavioural reaction of Striped Legless Lizards to fire is also unknown, although it seems likely that survivors would either move into unburnt areas or remain relatively inactive in the soil or under rocks until the vegetation recovers enough to provide shelter (Smith & Roberston 1999).
Burning is not necessarily negative for the species and in most situations a degree of burning is required as a management tool. Burning regimes with a frequency greater than once every five years are likely to negatively influence Striped Legless Lizard survivorship (O'Shea 2005). However, it appears that the degree of mortality may vary with timing and the amount of soil cracking and fire type, where autumn/winter burns and wild fire are low impact and spring/summer and control/convection burns are high impact (Coulson 1990; O'Shea 2005).
Smith and Robertson (1999) report that there may be a number of natural and introduced predators of this species. It is assumed that a range of native predators including snakes, other lizards, raptors, magpies and other predatory birds, and possibly dunnarts (Sminthopsis spp.), will prey on Striped Legless Lizards, but the extent of this predation is unknown. High densities of introduced predators may be more of a concern, as urban development surrounds many Striped Legless Lizard populations. Anecdotal evidence suggests that foxes may prey upon the species (S. Walton n.d., pers comm., cited in Smith & Robertson 1999), and in urban areas cats may also be a threat to populations. Despite this, whether or not predation is a significant threatening process is yet to be thoroughly investigated as this species is both highly cryptic and secretive (Smith & Robertson 1999).
Ten specific conservation objectives were outlined in the species recovery plan prepared by Smith and Robertson (1999). Broadly, these conservation objectives addressed the need to increase our knowledge of the biological and ecological requirements of this species and its distribution, as well as increasing community awareness.
Conservation objectives as outlined in the recovery plan for the Striped Legless Lizard (Delmar impar) (Smith & Robertson 1999):
- Establish and maintain national forums for the discussion and organization of the conservation of the Striped Legless Lizard across its natural distribution.
- Determine the distribution of potential Striped Legless Lizard habitat.
- Determine the current distribution and abundance of Striped Legless Lizards in Victoria, NSW, the ACT and SA.
- Establish a series of reserves and other managed areas such that viable populations are maintained across the known distribution of the species.
- Determine the habitat use and ecological requirements of Striped Legless Lizards.
- Identify the nature and extent of the threatening processes affecting Striped Legless Lizards.
- Undertake a program of research and monitoring to provide a basis for adaptive management of Striped Legless Lizards.
- Increase community awareness and involve the community in aspects of the recovery program.
- Assess the need for salvage and translocation, determine their feasibilities, develop protocols and undertake a trial translocation if appropriate.
- Ensure that captive population(s) are used to support education and research elements of the Recovery Plan.
A revised national recovery plan is currently in development.
A National Recovery Team (NRT) for the Striped Legless Lizard was established in 1995, and has been coordinating national survey and research efforts. The outcome of these research and survey efforts have primarily been planned and implemented by two regional working groups: the Victorian Striped Legless Lizard Working Group (VSLLWG), and the ACT and NSW Striped Legless Lizard Regional Working Group (SLLRWG). These working groups are the source of most of the biological and distributional information available for this species (Smith & Robertson 1999).
Smith and Robertson (1999) noted that actions towards meeting recovery objectives was well underway. In particular, research into aspects of the species' habitat relationships has been the focus of much attention in an attempt to identify management requirements for the species. A population and habitat viability analysis (PHVA) was conducted to determine factors important in the population dynamics (ARAZPA 1996; Smith & Robertson 1999) and movements, dietary preferences, and alternative trapping techniques have also been investigated. However, basic demographic parameters such as mortality, recruitment growth and life span remain largely unknown, as do the effects of habitat disturbance factors (i.e. fire, grazing and weed invasion) (Smith & Robertson 1999). The principle hurdle in overcoming this knowledge gap regarding this species' habitat and biology is the difficulty in identifying and monitoring this species (i.e. trapping and tagging of this species).
An ecological burning regime was trialed in reserves at the Royal Australian Air Force (RAAF) Williams Laverton Base in Victoria, in order to maintain an appropriate habitat for this species (Mueck et al. 1998). Regular burning establishes open tussock grassland, a vegetation structure which is considered to provide suitable habitat for the Striped Legless Lizard. Ideally, burning should be patchy and not cover more than 50% of the grassland in any year. Burning up to one third of each grassland area each year is considered by Mueck and colleagues (1998) to be acceptable for the management of this species.
At the same location Mueck and colleagues (1998) suggested a program to salvage Striped Legless Lizards from areas outside these reserves (i.e. on the Commonwealth Defense land) that involves the following:
- Scraping of the topsoil conducted by back-hoe in a sample area of high quality Danthonia and Stipa grassland
- Locating and capturing any animals exposed by the scraping
- Add animals salvaged from the site to the captive colony at the Melbourne Zoo for ecological research and for potential relocation to other conservation reserves (Mueck et al. 1998).
The conservation of Striped Legless Lizards and their habitat will assist in the conservation of natural temperate grassland, which is one of Australia's most threatened ecosystems. Many other threatened flora and fauna species associated with natural temperate grasslands will benefit greatly from the protection and management of Striped Legless Lizard native habitat. The promotion of grassland conservation, however, is problematic because grasslands do not have the broad public appreciation of forests, rivers or wetlands. Having a species such as the Striped Legless Lizard as a well-known and well-liked 'flagship' can be invaluable in the overall conservation of native temperate grasslands (Smith & Robertson 1999).
Government funded projects
McCallums Creek Landcare Group (Victoria) received $4150 of funding through the Threatened Species Network Community Grants in 200607 for fencing of 2 ha to protect the lizards from persistent grazing, and the development of a management plan with the assistance of professional advisers.
Hamilton Coleraine Rail Reserve Committee Inc (Victoria) received $5400 of funding through the Threatened Species Network Community Grants in 200607 for the protection and rehabilitation of habitat, fencing to exclude stock, weed control, replanting of degraded sections with native grasses, monitoring to further map the range of this species at the site, and signage for visitors to the Reserve.
Upper Campaspe Combined Landcare Group (Victoria) received $2150 of funding through the Threatened Species Network Community Grants in 200001 for fencing of the Lake Eppalock foreshore to prevent sheep access to remnant grassland habitat.
The Upper Goulburn Catchment Group (Victoria) received $4900 of funding through the Threatened Species Network Community Grants in 200102 for the enhancement of known habitat of this species through removal of weeds, community education, monitoring/survey work, and encouragement of landholders to maintain existing habitats on their lands at Yea cemetery and local roadsides.
The Wannon Conservation Society (Victoria) received $4236 of funding through the Threatened Species Network Community Grants in 200203 for determining the south-western limit of the species distribution and the establishment of habitat preferences, and the provision of advice to landholders to help manage populations on private land.
Community Groups in Castlemaine Zone (Victoria) received $28 500 of funding through the Threatened Species Network Community Grants in 200203 for the protection of state-listed ecological communities including grassy woodlands and creekline grassy woodlands to conserve and enhance habitat for threatened species, habitat restoration, weed and predator control.
Friends of the Striped Legless Lizard (FOSLL) (Victoria) received $6200 of funding through the Threatened Species Network Community Grants in 200304 for the repair of habitat for this species, seed orchard beds and signage to educate the community about threatened plants and animals in the region.
Friends of Merri Creek (Victoria) received $6503 of funding through the Threatened Species Network Community Grants in 200405, part of which was for restoration and expansion of habitat for the Striped legless lizard, and for restoration of a native grassland community.
Management documents for the Striped Legless Lizard include:
- National Recovery Plan for the Striped Legless Lizard (Delma impar): 1999-2003 (Smith & Robertson 1999) (curently under revision).
- Striped Legless Lizard (Delma impar): A vulnerable species. Action Plan No. 2 (ACT Government 1997g).
- Striped Legless Lizard - profile (NSW DECC 2005am).
- Flora & Fauna Guarantee Action Statement no. 17: Striped Legless Lizard Delma impar (Webster et al. 2003).
- Threat Abatement Plan for predation by the European red fox (DEWHA) (2008adf).
- Threat Abatement Plan for predation by feral cats (DEWHA) (2008adg).
The following table lists known and perceived threats to this species. Threats are based on the International Union for Conservation of Nature and Natural Resources (IUCN) threat classification version 1.1.
|Threat Class||Threatening Species||References|
|Agriculture and Aquaculture:Agriculture and Aquaculture:Land clearing, habitat fragmentation and/or habitat degradation||
The Action Plan for Australian Reptiles (Cogger, H.G., E.E. Cameron, R.A. Sadlier & P. Eggler, 1993) [Cwlth Action Plan].
National Recovery Plan for the Striped Legless Lizard (Delma impar): 1999-2003 (Smith, W.J.S. & P. Robertson, 1999) [Recovery Plan].
|Agriculture and Aquaculture:Livestock Farming and Grazing:Grazing modified pastures and associated habitat changes||National Recovery Plan for the Striped Legless Lizard (Delma impar): 1999-2003 (Smith, W.J.S. & P. Robertson, 1999) [Recovery Plan].|
|Agriculture and Aquaculture:Livestock Farming and Grazing:Grazing pressures and associated habitat changes||National Recovery Plan for the Striped Legless Lizard (Delma impar): 1999-2003 (Smith, W.J.S. & P. Robertson, 1999) [Recovery Plan].|
|Agriculture and Aquaculture:Livestock Farming and Grazing:Habitat loss and modification due to clearance of native vegetation and pasture improvements||The Impact of Global Warming on the Distribution of Threatened Vertebrates (ANZECC 1991) (Dexter, E.M., A.D. Chapman & J.R. Busby, 1995) [Report].|
|Biological Resource Use:Hunting and Collecting Terrestrial Animals:Harvesting for scientific purposes||National Recovery Plan for the Striped Legless Lizard (Delma impar): 1999-2003 (Smith, W.J.S. & P. Robertson, 1999) [Recovery Plan].|
|Climate Change and Severe Weather:Droughts:Drought|
|Invasive and Other Problematic Species and Genes:Invasive Non-Native/Alien Species:Competition and/or habitat degradation||Oryctolagus cuniculus (Rabbit, European Rabbit)||The threat posed by pest animals to biodiversity in New South Wales (Coutts-Smith, A.J., P.S. Mahon, M. Letnic & P.O. Downey, 2007) [Management Plan].|
|Invasive and Other Problematic Species and Genes:Invasive Non-Native/Alien Species:Competition and/or habitat degradation||Nassella neesiana (Chilean Needle grass)||Weeds of National Significance Chilean Needle-grass (Nassella neesiana) Strategic Plan (Agriculture & Resources Management Council of Australia & New Zealand, Australian & New Zealand Environment & Conservation Council and Forestry Ministers, 2001i) [Threat Abatement Plan].|
|Invasive and Other Problematic Species and Genes:Invasive Non-Native/Alien Species:Competition and/or predation||Vulpes vulpes (Red Fox, Fox)|
|Invasive and Other Problematic Species and Genes:Invasive Non-Native/Alien Species:Competition and/or predation||Felis catus (Cat, House Cat, Domestic Cat)|
|Natural System Modifications:Fire and Fire Suppression:Inappropriate and/or changed fire regimes (frequency, timing, intensity)|
ACT Government (1997g). Striped Legless Lizard (Delma impar). Action Plan No. 2. [Online]. Canberra: Environment ACT. Available from: http://www.environment.act.gov.au/__data/assets/pdf_file/0005/234473/actionplans2.pdf.
ACT Government (2005a). A Vision Splendid of the Grassy Plains Extended: ACT Lowland Native Grassland Conservation Strategy. [Online]. Action Plan No. 28. Canberra: Arts, Heritage and Environment. Available from: http://www.environment.act.gov.au/cpr/conservation_and_ecological_communities/grassland_conservation_strategy.
Anon (2002a). Striped legless lizard field day. Alexandra Eildon Marysville Standard. July 24.
Australasian Regional Association of Zoological Parks and Aquaria (ARAZPA) (1996). Population and Habitat Viability assessment (PHVA) for the striped legless lizard Delma impar. Workshop held in Canberra, Australia. 30 July - 2 August 1996. Australasian Regional Association of Zoological Parks and Aquaria, ACT Parks and Conservation Service, Striped Legless Lizard Working Group, and Conservation Breeding Specialist Group (SSC/IUCN).
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This database is designed to provide statutory, biological and ecological information on species and ecological communities, migratory species, marine species, and species and species products subject to international trade and commercial use protected under the Environment Protection and Biodiversity Conservation Act 1999 (the EPBC Act). It has been compiled from a range of sources including listing advice, recovery plans, published literature and individual experts. While reasonable efforts have been made to ensure the accuracy of the information, no guarantee is given, nor responsibility taken, by the Commonwealth for its accuracy, currency or completeness. The Commonwealth does not accept any responsibility for any loss or damage that may be occasioned directly or indirectly through the use of, or reliance on, the information contained in this database. The information contained in this database does not necessarily represent the views of the Commonwealth. This database is not intended to be a complete source of information on the matters it deals with. Individuals and organisations should consider all the available information, including that available from other sources, in deciding whether there is a need to make a referral or apply for a permit or exemption under the EPBC Act.
Citation: Department of the Environment (2014). Delma impar in Species Profile and Threats Database, Department of the Environment, Canberra. Available from: http://www.environment.gov.au/sprat. Accessed Sun, 31 Aug 2014 04:45:20 +1000.