|Scientific Name:||Macaca mulatta|
|Species Authority:||(Zimmermann, 1780)|
Macaca brachyurus (Elliot, 1909)
Macaca brevicaudatus (Elliot, 1913)
Macaca erythraea (Shaw, 1800)
Macaca fulvus (Kerr, 1792)
Macaca lasiotus (Gray, 1868)
Macaca littoralis (Elliot, 1909)
Macaca mcmahoni Pocock, 1932
Macaca nipalensis Hodgson, 1840
Macaca oinops Hodgson, 1840
Macaca rhesus (Audebert, 1798)
Macaca sancti-johannis (Swinhoe, 1866)
Macaca siamica Kloss, 1917
Macaca tcheliensis (Milne-Edwards, 1872)
Macaca vestita (Milne-Edwards, 1892)
Macaca villosa (True, 1894)
|Taxonomic Notes:||This species has been revised by Fooden (2000), who regards M. mulatta as monotypic. The molecular differences identified among M. mulatta populations (Melnick et al. 1993; Morales and Melnick 1998; Tosi 2000; Tosi et al. 2000, 2002, 2003; Zhang and Shi 1993) are alone not consistent enough to conclusively define any subspecies.|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||Timmins, R.J., Richardson, M., Chhangani, A. & Yongcheng, L.|
|Reviewer(s):||Mittermeier, R.A. & Rylands, A.B. (Primate Red List Authority)|
This species is listed as Least Concern in view of its wide distribution, presumed large population, is tolerant of a broad range of habitats, and because it is unlikely to be declining at anything close to the rate required to qualify for listing in a threatened category.
|Previously published Red List assessments:|
|Range Description:||The species as a whole is found throughout most of southern Asia, in eastern Afghanistan, Bangladesh, Bhutan, central and southern China (Anhui, Fujian, Guangdong, Guangxi, Guizhou, Hebei, Henan, Hubei, Hunan, Shaanxi, Sichuan, Tibet, and Yunnan, as well as the island of Hainan), northern and central India (in the states of Andhra Pradesh, Arunachal Pradesh, Assam, Bihar, Chattisgarh, Gujarat, Haryana, Himachal Pradesh, Jammu and Kashmir, Jharkand, Madhya Pradesh, Maharashtra, Manipur, Meghalaya, Mizoram, Nagaland, Orissa, Punjab, Rajasthan, Sikkim, Tripura, Uttaranchal, Uttar Pradesh and West Bengal), Lao PDR, Myanmar, Nepal, northern Pakistan, northern Thailand, and Viet Nam. |
It occurs to the north of the Krishna River in central and eastern India and to the north of the lower Tapti River in western India, north into Afghanistan, Nepal, Sikkim, Bhutan, and northeast into China, where it extends to the Yangtze and north of its middle course to about 33°N, 110°E. It is absent north of the lower Yangtze, but there is an additional, possibly introduced population in northern China north of the lower Hwang He (Yellow River), formerly occurring as far as Beijing (Groves 2001).
There are introduced populations (mostly not mapped) in areas within this region as well as outside it, for instance south of the Krishna River in India; Kowloon and a few small islands near Hong Kong; and to various other locations worldwide, including parts of Florida, USA and on Cayo Santiago island near Puerto Rico (M. Richardson pers. comm.).
Native:Afghanistan; Bangladesh; Bhutan; China; India; Lao People's Democratic Republic; Myanmar; Nepal; Pakistan; Thailand; Viet Nam
Introduced:Hong Kong; United States (Florida)
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||This species is widely distributed in south, southeast and east Asia. Populations are sizable, but increasingly commensal with humans, resulting in some fragmentation of the distribution (Molur et al. 2003). It can be abundant in many places, including in cities. Hunting of this species in Lao PDR and Viet Nam has severely depressed populations in these countries although it still remains widespread. In Namdapha National Park, India, this species was found to have a group density of 0.44 groups/km2, with an average group size of 12.3 individuals (Chetry et al. 2003). The average group size in other parts of India is much higher (Siddiqui and Southwick 2004). Srivastava and Mohnot (2001) consider this species to be rare in the forests of north-eastern India.|
|Current Population Trend:||Unknown|
|Habitat and Ecology:||This species is diurnal and omnivorous, and alternatively arboreal and terrestrial. It resides in a range of habitats, including temperate coniferous, moist and dry deciduous, bamboo, and mixed forests, mangroves, scrub, rainforest, and around human habitations and developments, including cultivated areas, temples, and roadsides (Choudhury 2001; Srivastava and Mohnot 2001). In Pakistan this monkey remains in mountainous regions with forest cover; it is typically associated with Himalayan moist temperate forest (Roberts 1997). It is found at elevations up to 4,000 m (Molur et al. 2003). Due to hunting in Lao PDR and Viet Nam the species does not occur in commensal situations there, and is restricted to forest areas where it is generally associated with riverine environments over a range of altitudes (Timmins pers. comm.). In western and northern parts of its range it seems to occur in a wider array of environments. It is highly adaptable to man-made habitat. Its generation time is 12 years (Molur et al. 2003).|
This species is generally unthreatened, though its original habitat is increasingly being lost to development. While M. mulatta exists easily around humans, the increasing level of cohabitation has been associated with waning levels of human tolerance for the animals (Molur et al. 2003). Confiscation for laboratory testing is a mostly localized threat, but it is considerable in certain areas (A. Kumar pers. comm.). Capture and release of laboratory and “problem monkeys” from rural and urban areas into natural forests is a major threat to wild macaques.
In Lao PDR and Viet Nam the major threat to the species is hunting, although loss of forest in river valleys has also likely impacted the species (R. Timmins pers. comm.). In Indochina hunting pressure is high, and thus tolerance to human disturbance is low.
Introduction, through release of confiscated M. fasicularis, is at least a localized threat in parts of the species' Viet Namese range (R. Timmins pers. comm.). Tolerance of the species varies locally, from heavily hunted and persecuted, to worshipped and fed.
This species is listed on CITES Appendix II. It is also listed in Schedule III in the Bangladesh Wildlife (Preservation) (Amendment) Act, 1974 and in Schedule I, Part I in the Indian Wildlife (Protection) Act (amended up to 2002), on Category II of the Chinese Wildlife Protection Act (1989), and is protected with all other primates in the Nepalese National Parks and Wildlife Conservation Act, 1973. Protection status varies widely throughout the species range.
Rhesus macaques reside in a large number of protected areas throughout their range.
Chetry, D., Medhi, R., Biswas, J., Das, D. and Bhattacharjee, P. C. 2003. Nonhuman primates in the Namdapha National Park, Arunachal Pradesh, India. International Journal of Primatology 24(2): 383-388.
Choudhury, A. 2001. Primates in Northeast India: An overview of their distribution and conservation. ENVIS Bulletin: Wildlife and Protected Areas 1(1): 92-101.
Fooden, J. 1964. Rhesus and crab-eating macaques: intergradation in Thailand. Science 143(3604): 363-365.
Fooden, J. 2000. Systematic review of the rhesus macaque, Macaca mulatta (Zimmermann, 1780). Fieldiana Zoologica 96: 1–180.
Groves, C.P. 2001. Primate Taxonomy. Smithsonian Institution Press, Washington, DC, USA.
Habibi, K. 2004. Mammals of Afghanistan. Zoo Outreach Organisation/USFWS, Coimbatore, India.
Jiang, H., Wang, Y. and Ma, S. 1991. Taxonomic revision and distribution of subspecies of rhesus monkey (Macaca mulatta) in China. Zoological Research 12: 241-247.
Jiang, H., Zhenhe, L., Yongzu, Z. and Southwick, C. 1991. Population ecology of rhesus monkeys (Macaca mulatta) at Nanwan Nature Reserve, Hainan, China. American Journal of Primatology 25(4): 207-217.
Melnick, D. J., Hoelzer, G. A., Absher, R. and Ashley, M. V. 1993. MtDNAdiversity in rhesus monkeys reveals overestimates of divergence time and paraphyly with neighboring species. Molecular Biology and Evolution 10: 282–295.
Molur, S., Brandon-Jones, D., Dittus, W., Eudey, A., Kumar, A., Singh, M., Feeroz, M. M., Chalise, M., Priya, P. and Walker, S. 2003. Status of South Asian Primates: Conservation Assessment and Managment Plan Report. Workshop Report, 2003. Zoo Outreach Organization/CBSG-South Asia, Coimbatore, India.
Morales, J. C. and Melnick, D. J. 1998. Phylogenetic relationships of the macaques (Cercopithecidae: Macaca), as revealed by high resolution restriction site mapping of mitochondrial ribosomal genes. Journal of Human Evolution 34: 1-23.
Neville, M. 1968. Ecology and activity of Himalayan foothill rhesus monkeys (Macaca mulatta). Ecology 49(1): 110-123.
Roberts, T.J. 1977. The Mammals of Pakistan. Ernest Benn, London, UK.
Srivastava, A. and Mohnot, S. M. 2001. Distribution, conservation status and priorities for primates in Northeast India. ENVIS Bulletin: Wildlife and Protected Areas 1(1): 102-108.
Tosi, A. J. 2000. Evolutionary Relationships Among Members of the Genus Macaca as Inferred From Paternal, Maternal, and Biparental Molecular Markers. Columbia University.
Tosi, A. J., Morales, J. C. and Melnick, D. J. 2000. Comparison ofY-chromosome and mtDNA phylogenies leads to unique inferences of macaque evolutionary history. Molecular Phylogenetics and Evolution 17: 133–144.
Tosi, A. J., Morales, J. C. and Melnick, D. J. 2002. Y-chromosome and mitochondrial markers in Macaca fascicularis indicate introgression with M. mulatta and a biogeographic barrier in the Isthmus of Kra. International Journal of Primatology 23: 161–178.
Tosi, A. J., Morales, J. C. and Melnick, D. J. 2003. Paternal, maternal, and biparental molecular markers provide unique windows onto the evolutionary history of macaque monkeys. Evolution 57: 1419–1435.
Zhang, Y. P. and Shi, L. M. 1993. Phylogeny of rhesus monkeys (Macaca mulatta) as revealed by mitochondrial DNA restriction enzyme analysis. International Journal of Primatology 14: 587–605.
|Citation:||Timmins, R.J., Richardson, M., Chhangani, A. & Yongcheng, L. 2008. Macaca mulatta. The IUCN Red List of Threatened Species 2008: e.T12554A3356486.Downloaded on 24 July 2016.|
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