|Scientific Name:||Nycticebus bengalensis|
|Species Authority:||(Lacépède, 1800)|
Nycticebus cinereus Milne-Edwards, 1867
Nycticebus incanus Thomas, 1921
Nycticebus tenasserimensis Elliot, 1913
|Taxonomic Notes:||This taxon was formerly considered a subspecies of Nycticebus coucang, with which there is a small hybridization zone in peninsular Thailand. No subspecies are recognized. Considerable variation exists in body size and coat colour in this taxon.|
|Red List Category & Criteria:||Vulnerable A2acd+3cd+4acd ver 3.1|
|Assessor/s:||Streicher, U., Singh, M., Timmins, R.J. & Brockelman, W.|
|Reviewer/s:||Mittermeier, R.A. & Rylands, A.B. (Primate Red List Authority)|
Listed as Vulnerable as, due to loss of habitat and severe pressures from hunting, there is more than 30% reduction in population over three generations (approximately 21-24 years). The species is predicted to decline by more than 30% in the next three generations over its entire range due to continuing hunting pressures and loss of habitat.
|Range Description:||This species occurs in Bangladesh, Cambodia, China (southern Yunnan and possibly southern Guangxi), north-eastern India (Arunachal Pradesh, Assam, Manipur, Meghalaya, Mizoram, Nagaland, and Tripura), Lao PDR, Myanmar (including the Mergui Archipelago), Thailand, and Viet Nam (except the south). It may possibly occur as well in northern Peninsular Malaysia.|
Native:Bangladesh; Cambodia; China; India; Lao People's Democratic Republic; Myanmar; Thailand; Viet Nam
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||In Lao PDR, the population seems to be fairly undisturbed and occurs in large forest tracts (R. Timmins pers. comm.). Duckworth (1994) and Ratajszczak (1998) both reported the species as being very rare in Lao PDR, with the former reporting abundance indices of about 0.30-0.65/km, and the latter detecting only three after a several week survey. It is recorded in two areas in Bangladesh: Chittagong and Sylhet (Molur et al. 2003). In India, the encounter rates vary from 0.1 to 0.77/km (Radhakrishna et al. 2006). In Viet Nam, the populations are severely reduced and have disappeared from many forests (Fitch-Snyder and Thanh 2002; V. Thanh pers. comm.). In Cambodia it is widespread, though a long-term survey by Starr has also failed to detect this species in most forests. It is also widespread in Thailand (W. Brockelman pers. comm.), though an on-going study by Pliwsungnoen has found that they are absent from many forests, and are at very low densities when they are present (Pliwsungnoen pers. comm.).|
|Habitat and Ecology:||
This is an arboreal, nocturnal species that inhabits tropical evergreen rainforest, semi-evergreen forest, and moist deciduous forest. In Viet Nam it is found only in secondary forests, and on the edge of primary forests; they are also known to come close to agricultural fields and plantations (V. Thanh pers. comm.). It ranges from sea level (U. Streicher pers. comm.) up to 2,400 m (Choudhury 2001). It feeds on fruits and gums, but very few insects as compared to slender or pygmy lorises (U. Streicher pers. comm.).
This animal?s life span is about 15 years, and generation time is 7-8 years. Females give birth to one offspring per litter once every two years in semi-wild conditions (Rowe 1996). In captivity, this rate may be slightly higher (U. Streicher pers. comm.).
|Major Threat(s):||The major threats that this species' habitat faces include farming, timber removal, human settlement, road building, dams, power lines, fragmentations, soil loss and erosion, and deliberately set fires. They are hunted and traded for food, traditional ?medicine,? sport, and as pets (Molur et al. 2003; Nekaris and Nijman 2007; V. Thanh and U. Streicher pers. comm.). Road kills represent another threat to this species.|
This species is listed in Bangladesh as Schedule III in the Bangladesh Wildlife (Preservation) (Amendment) Act, 1974. In India, it is listed in Schedule I, part I, under the Indian Wildlife Protection Act, 1972 amended up to 2002. This species is protected in Thailand under the Wildlife Protection of 1992; in China it is Class I, and is given the highest protection in Viet Nam under the Wildlife Protection Law (List IB, Decree 32, 2006) on a par with tigers, elephants and bears. In Cambodia, it is protected under law 359 of the Ministry of Forestry and Fisheries, 1994.
This species is found in a large number of protected areas throughout its range, but possibly at low numbers. Actual surveys rather than anecdotal reports are necessary to determine the true abundance of this species in the wild (Nekaris et al. 2008). The species has been recently transfer from Appendix II to Appendix I of CITES (Nekaris and Nijman 2007).
|Citation:||Streicher, U., Singh, M., Timmins, R.J. & Brockelman, W. 2008. Nycticebus bengalensis. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.2. <www.iucnredlist.org>. Downloaded on 20 April 2014.|
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