|Scientific Name:||Prionailurus bengalensis|
|Species Authority:||(Kerr, 1792)|
|Infra-specific Taxa Assessed:|
|Taxonomic Notes:||On the basis of morphological analysis, Groves (1997) suggested recognition of several distinct island subspecies, including:
P. b. borneoensis Brongersma, 1936: Borneo
P. b. heaneyi Groves, 1997: Palawan island, Philippines
P. b. javenensis (Desmarest, 1816): Java and Bali
P. b. rabori Groves, 1997: Negros, Cebu and Panay islands, Philippines
P. b. sumatranus (Horsfield, 1821): Sumatra and the offshore island of Tebingtinggi
Although one mainland Asian subspecies is generally recognized, the nominate P. b. bengalensis (Kerr, 1792) (Groves 1997), a number of mainland Asian subspecies have been classically described, including the Amur Leopard Cat P. b. euptilurus of the Korean Peninsula, Russian Far East and northeastern China. It was earlier proposed as a distinct species based on morphological differences from southeast Asian specimens, but Chinese specimens were shown to be similar and this is not recognized (Wozencraft 2005).
The Iriomote Cat P. b. iriomotensis, from Japan's Iriomote island, was also originally described as a distinct species based on morphology (Imaizumi 1967), but based on genetic analysis is considered a subspecies of Leopard Cat (Masuda and Yoshida 1995, Johnson et al. 1999, Eizirik et al. submitted).
Patterns of genetic variation in the Leopard Cat is currently under study (Shu-Jin Luo pers. comm. 2008), and should improve understanding of subspeciation in this widespread species which occurs on more islands than any other felid.
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor/s:||Sanderson, J., Sunarto, S., Wilting, A., Driscoll, C., Lorica, R., Ross, J., Hearn, A., Mujkherjee, S., Khan, J.A., Habib, B. & Grassman, L.|
|Reviewer/s:||Nowell, K., Breitenmoser-Wursten, C., Breitenmoser, U. (Cat Red List Authority) & Schipper, J. (Global Mammal Assessment Team)|
The Leopard Cat is a widespread and relatively common species (Nowell and Jackson 1996, Sunquist and Sunquist 2002), although some island subspecies are included in the Red List. Although there is a declining population trend in parts of its range due to habitat loss and hunting, the species is stable in many areas, even thriving in some altered habitats including oil palm and sugar cane plantations (IUCN Cats Red List Workshop 2007).
|Range Description:||The leopard cat is a widespread species in Asia. It is found throughout most of India west into Pakistan and Afghanistan (Habibi 2004), through the Himalayan foothills, across most of China, and north to the Korean peninsula and into the Russian Far East (Nowell and Jackson 1996). It is found throughout Southeast Asia, and on the islands of Sumatra, Java, Borneo and Taiwan. It is found on numerous small offshore islands of mainland Asia (Nowell and Jackson 1996, Sunquist and Sunquist 2002). The leopard cat is the only wild felid found in the Japan, where it occurs on the small islands Tsushima and Iriomote, and the Philippines, where it occurs on the islands of Palawan, Panay, Negros and Cebu. In the Philippines, there are recent (2007) unconfirmed reports from the island of Masbate. It should be present in Guimaras due to proximity to Negros and Panay, but no presence was reported, and is therefore presumed to be extinct (R. Lorica and W. Oliver, unpub.).|
Native:Afghanistan; Bangladesh; Bhutan; Brunei Darussalam; Cambodia; China; Hong Kong; India; Indonesia (Jawa, Kalimantan, Sumatera); Japan (Nansei-shoto); Korea, Democratic People's Republic of; Korea, Republic of; Lao People's Democratic Republic; Malaysia; Myanmar; Nepal; Pakistan; Philippines; Russian Federation; Singapore; Taiwan, Province of China; Thailand; Viet Nam
|Range Map:||Click here to open the map viewer and explore range.|
The leopard cat is the most frequently recorded small cat across most of its wide range, in comparison with sympatric species (Nowell and Jackson 1996, Duckworth et al. 1999, Holden 2001, Duckworth et al. 2005, Lynam et al. 2006, Yasuda et al. 2007), and with its broad distribution has an abundant population. However, it is probably declining due to habitat loss and hunting. Large numbers of leopard cat furs were exported from China (averaging 200,000 skins per year in the late 1980s) (Nowell and Jackson 1996). Higher survival rates (92%) were recorded in a protected area with little human influence, compared with lower rates in areas with greater human activity (53-82%) (Haines et al. 2004). While the leopard cat is more tolerant of disturbed areas than other small Asian felids, it likely undergoes higher mortality in such areas.
Island populations are most at risk of extinction, with the Iriomote cat P.b. iriomotensis listed as Critically Endangered, and the Visayan leopard cat P.b. rabori of the Philippine islands of Panay, Negros, Cebu and possibly Masbate listed a Vulnerable. The small population (approximately 100) on Japan's 710 km² Tsushima Island, considered the same subspecies as occurs in northeastern mainland Asia, has decreased over the last 30-40 years (Izawa et al. 2007).
|Habitat and Ecology:||
The species can range up to 3,000 m in parts of its range, which extends into the Himalayas along river valleys. It occurs in a broad spectrum of habitats, from tropical rainforest to temperate broadleaf and, marginally, coniferous forest, as well as shrub forest and successional grasslands. The northern boundaries of its range are limited by snow cover; the leopard cat avoids areas where snow is more than 10 cm deep. It is not found in the cold steppe grasslands, and generally does not occur in arid zones, although there are a few records from relatively dry and treeless areas in Pakistan. Leopard cats occur commonly in dense secondary growth, including logged areas, and have been found in agricultural and forest (rubber tree, oil palm, sugarcane) plantations. The species can live close to rural settlements. Leopard cats are excellent swimmers, and have successfully colonized offshore islands throughout their range (Nowell and Jackson 1996; Sunquist and Sunquist 2002).
In the most comprehensive study, based on a large sample size of 20 radio-collared cats in Thailand's Phu Khieu Wildlife Sanctuary, mean home range size (95% MCP) was 12.7 km², larger than in other areas of Thailand (4.5 km²) (Grassman et al. 2005), on Borneo (3.5 km²: Rajaratnam 2000), or on Japan's Iriomote island (Schmidt et al. 2003). There was no significant difference between male and female home range size. Open and closed forest habitats were used in proportion to their occurrence, and activity patterns showed crepuscular and nocturnal peaks. On Borneo, Rajaratnam et al. (2007) found that leopard cats hunted rodents in oil palm plantations, and used forest fragments for resting and breeding. Murids dominate the diet (85-90%: Grassman et al. 2005b, Rajaratnam et al. 2007). Other small mamals, eels and fish have also been reported, as well as occasional scavenging of carrion (Nowell and Jackson 1996).
|Major Threat(s):||In China, the centre of its range, commercial exploitation has been heavy: hundreds of thousands of Leopard Cat skins per year were exported in the 1980s. Although commercial trade is much reduced, the species continues to be hunted throughout most of its range for fur, for food, and as pets. They are also widely viewed as poultry pests and killed in retribution. Island populations are small and seriously threatened in the Philippines and Japan. Leopard cats can hybridize with domestic cats, as is shown by the popular domestic breed, the "Bengal Cat" although most of these exotic cats are now bred from Bengal Cat stock rather than wild crosses (TICA, The International Cat Association, 2012). . Hybridization in the wild has been reported, but is not considered a significant threat. Although the species is less dependent on forest cover than others, habitat loss and fragmentation is still a major threat across most of its Asian range (Nowell and Jackson 1996).|
|Conservation Actions:||Included on CITES Appendix II; populations in Bangladesh, India and Thailand are included on Appendix I (as Prionailurus bengalensis bengalensis). The species is protected at the national level over part of its range, with hunting prohibited in Bangladesh, Cambodia, Hong Kong, India, Indonesia, Japan, Malaysia, Myanmar, Nepal, Pakistan, Philippines, Russia, Thailand and Taiwan, and hunting and trade regulations in place in South Korea, Lao PDR and Singapore (Nowell and Jackson 1996, A. Wilting pers. comm. 2008). The species is on Afghanistan’s 2009 Protected Species List, banning all hunting and trading of this species within the country. It is found in numerous protected areas.|
|Citation:||Sanderson, J., Sunarto, S., Wilting, A., Driscoll, C., Lorica, R., Ross, J., Hearn, A., Mujkherjee, S., Khan, J.A., Habib, B. & Grassman, L. 2008. Prionailurus bengalensis. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.2. <www.iucnredlist.org>. Downloaded on 10 March 2014.|
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