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Listing Advice Perameles Fasciata Liverpool Plains Striped Bandicoot

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Listing Advice Perameles Fasciata Liverpool Plains Striped Bandicoot THREATENED SPECIES SCIENTIFIC COMMITTEE Established under the Environment Protection and Biodiversity Conservation Act 1999 The Minister approved this listing advice and retained this species in the Extinct category, effective from 02/02/2021 Listing Advice Perameles fasciata Liverpool Plains Striped Bandicoot Taxonomy Conventionally accepted as Perameles fasciata Gray, 1841. As part of a subspecies complex, Perameles fasciata (Liverpool Plains Striped Bandicoot) was previously described as Perameles bougainville fasciata. This complex consisted of three extinct species: the Liverpool Plains Striped Bandicoot, P. notina (South-eastern Striped Bandicoot) (previously P. b. notina), and P. myosuros (Marl) (previously P. b. myosuros), together with the extant P. b. bougainville (Shark Bay Bandicoot). Recently, Travouillon & Phillips (2018) revised the taxonomy, elevating the three extinct species to full species level, stating that they are sufficiently distinct to warrant elevation. This revision is recognised by the Australian Faunal Directory. Summary of assessment Conservation status Following a formal review of the listing status of the Liverpool Plains Striped Bandicoot, the Threatened Species Scientific Committee (the Committee) has determined that there is sufficient evidence to retain the Liverpool Plains Striped Bandicoot in the Extinct category under the Environmental Protection and Biodiversity Conservation Act 1999 (EPBC Act). Species can be listed under state and territory legislation. For information on the listing status of this species under relevant state or territory legislation, see http://www.environment.gov.au/cgi- bin/sprat/public/sprat.pl Reason for listing assessment by the Threatened Species Scientific Committee The Liverpool Plains Striped Bandicoot was listed as Extinct under the predecessor to the EPBC Act the Endangered Species Protection Act 1992 and transferred to the EPBC Act in July 2000. This advice follows assessment of new information provided to the Committee to list species included in the former Perameles bougainville subspecies complex. Public consultation Notice of the proposed amendment and a consultation document was made available for public comment for 31 business days between 31 July 2020 and 11 September 2020. Any comments received that were relevant to the listing of the species were considered by the Committee as part of the assessment process. Species/sub-species information Description The Liverpool Plains Striped Bandicoot resembled the other bandicoots in the former Perameles bougainville subspecies complex. However, there are few preserved specimens of the species available for examination, making it difficult to describe in detail (Woinarski et al. 2014a; Travouillon & Phillips 2018). Perameles fasciata (Liverpool Plains Striped Bandicoot) Listing Advice Page 1 of 10 From the available descriptions, the fur was a dark colour from above (being pencilled with black and yellow in equal portions), moderately long, and course. On the flanks, yellow outweighed black, and on the hindquarters, black prevailed as the dominant colour. On the rump, three broad, yellowish-white bars radiated down over the sides of the body. These bars were interrupted at the midline by a thick black band of fur that extended down the rump to the tip of the tail. From below, the fur was white. The muzzle was slender and long. Dark whiskers were present at the front of the snout, above the eye, and on the cheek below the eye. The ears were proportionally long (average 41 mm). The feet were white and elongated, with the three inner toes large, while the outer toes were reduced. The tail was also white, except for a line of black fur running along the upper surface (Gould 1863; Travouillon & Phillips 2018). The skull, ear, and tail length are the only body measurements recorded for the species. These measurements correspond to those of the Shark Bay Bandicoot (also known as the Western Barred Bandicoot) (Travouillon & Phillips 2018), suggesting that it was similarly small and lightly built. No head-body length or weight is recorded, but the Shark Bay Bandicoot has an average head-body length of 236 mm and weight of 244 g (Friend 2008). Distribution The Liverpool Plains Striped Bandicoot is known only from records in the Liverpool Plains, New South Wales (NSW) but may have had a more extensive distribution (Woinarski et al. 2014a). There are 14 records of the Liverpool Plains Striped Bandicoot in the Atlas of Living Australia. Only two are located in the Liverpool Plains region, with the remainder possibly other misidentified bandicoot species. The Liverpool Plains region forms an extensive tract of naturally treeless grasslands (Lang 2008), located south-west of Tamworth and bounded by the Great Dividing Range (east), the Warrumbungle Range (west), and the Liverpool Range (south). The climate of the Liverpool Plains is sub-humid with warm to hot summers and cool to mild winters. Two-thirds of the annual rainfall are received during the summer months, from October to March. Rainfall is variable with drought and floods likely to occur in any season (Lang 2008). Before European settlement, dominant plant species in the Liverpool Plains likely included Themeda avenacea (Native Oatgrass), Eulalia aurea (Silky Browntop), and Astrebla lappacea (Curly Mitchell grass) (Lang 2008). Scattered shrubs and clumps of trees often formed a transition zone between distinct grassland and adjacent woodland, which included Acacia pendula (Boree) and eucalypt species: E. conica (Fuzzy Box), E. populnea (Bimble Box), and E. melliodora (Yellow Box) (NSW Scientific Committee 2001; OEH 2017). Extinction date An extinction date is difficult to determine as collection data is poor and there was evident confusion of firsthand sources in identifying the different species of the former Perameles bougainville subspecies complex (firsthand observations compiled by Abbott (2008a) and Gould (1863)). Common names were often used interchangeably, and, in some instances, the provided distribution ranges do not match our current understanding. However, Woinarski et al. (2014a) proposed that extinction may have occurred around the mid-19th century, with the last known specimen collected in 1846. Relevant biology/ecology Little is known about the Liverpool Plains Striped Bandicoot. However, its ecology can be surmised from other known bandicoot species, which (notwithstanding their wide range of habitats) are considered an ecologically uniform group (Stodart 1977). Therefore, behaviours are likely to have been shared with the better known Shark Bay Bandicoot. Bandicoots are mainly nocturnal and solitary, with males occupying a larger home range than females. The home range for the Shark Bay Bandicoot is 2.5−14.2 ha for males and 1.4−6.2 ha for females. Bandicoots shelter during the day in concealed nests, constructed from grasses and other vegetation, and made in small hollows under shrubs (Richards 2004). Foraging at night, bandicoots feed predominantly on insects and their larvae, but they are opportunistic feeders Perameles fasciata (Liverpool Plains Striped Bandicoot) Listing Advice Page 2 of 10 and will also consume fruit, berries, seeds, and fungi. Prey is either dug out of the soil or gleaned from the surface (Lerner & Wilmoth 2014). As with all marsupials, bandicoot young are born at an early stage of development, usually after a gestation period of just 12 days, which is one of the shortest periods of any mammal. The average litter size for the Shark Bay Bandicoot is two but litters are recorded ranging from one to four (Richards 2012). Juveniles remain in the pouch for about 50 days before being weaned by the mother. By the time they are seven weeks old, young are covered with short hair and the eyes are open (Lerner & Wilmoth 2014). The Shark Bay Bandicoot has been recorded to live for over four years (Friend 2008). Threats The causes of decline and extinction of the Liverpool Plains Striped Bandicoot are unknown. However, likely contributing factors are surmised from threats known to have occurred shortly after European settlement in Australia. The assumption has been made that the threats that affect many bandicoot species would also have impacted on the Liverpool Plains Striped Bandicoot. Table 1: Probable causes of decline towards extinction for the Liverpool Plains Striped Bandicoot in approximate order of impact, based on available evidence. Threat factor Threat type and status Evidence base Introduced predators Predation by Suspected past Feral cats are thought to have been present feral cats (Felis throughout eastern NSW by the mid-19th century catus) (Abbott 2008b) and have been observed to greatly impact native mammals on the Liverpool Plains, with the magnitude of the threat increasing as the habitat became fragmented (Paull & Date1999). Predation by feral cats has been implicated in the extinction and ongoing decline of many terrestrial, non-volant, mammal species (Dickman 1993; Smith & Quin 1996; Woinarski et al. 2014c; Woinarski et al. 2015; Hardman et al. 2016; Davies et al. 2017; Radford et al. 2018; Woolley et al. 2019), with vertebrate prey up to four kg taken (Fancourt 2015). Woinarski et al. (2014c) considered predation by feral cats to be the most critical factor in the decline and extirpation of Australia’s mammal fauna. McKenzie et al. (2007) observed that bandicoots are particularly prone to predation, as they dwell on the ground’s surface and do not utilise shelter like arboreal, rock-dwelling, or burrowing
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