|Scientific Name:||Moschus berezovskii|
|Species Authority:||Flerov, 1929|
|Taxonomic Notes:||This species was revised by Wang et al. (1993). It is a well-defined species sharply distinct from the parapatric or marginally sympatric M. chrysogaster; see Grubb (1982).
Four subspecies are recognized by Grubb (2005):
M. b. berezovskii Flerov, 1929; Sichuan, Qinghai, Tibet
M. b. bjiangensis Wang & Li, 2003; northwestern Yunnan;
M. b. caobangis Dao, 1969; Yunnan, Guangxi, Guangdong, northern Viet Nam;
M. b. yunguiensis Wang & Ma, 1993; Yunnan-Guizhou highland, Hunan, Jiangxi; Wang (2003) lists an unnamed form as occurring in south Gansu, Ningxia, south Shaanxi, west Hubei and west Henan (Wang et al. 1993); Wemmer (1998).
Moschus anhuiensis has in the past been included in this species (Yang et al. 2003); it is still not clear whether or not the recognized subspecies are really part of this species. The subspecies M. b. caobangis is a good candidate for separate species status, but this has never been looked at (J.W. Duckworth pers. comm.). Until recently the Viet Namese population was considered to be M. moschiforus by Russian scientists (much literature follows this; J.W. Duckworth pers. comm.).
|Red List Category & Criteria:||Endangered A2cd ver 3.1|
|Assessor(s):||Wang, Y. & Harris, R.|
|Reviewer(s):||Brook, S.M. & McShea, W.J.|
This species is listed as Endangered because of a probable serious population decline, inferred to be more than 50% over the last three generations (approximately 21 years), caused by over-exploitation, shrinkage in distribution, habitat destruction and degradation. Although there are no direct data available regarding recent declining population rates, the above-mentioned rate of decline seems reasonable based on the high levels of harvesting and habitat loss. It should also be noted that the population in China was guessed at over one million in the 1960s; in 1978-1980 at less than 600,000; and in 1992 at 100,000 to 200,000 in 1992 (Sheng 1998), though the basis for these numbers is not clear. However, if this level of decline is roughly correct, then the species might even qualify for listing as Critically Endangered under criterion A2cd. No new information was received in 2014 to enable a full re-assessment of this species.
|Previously published Red List assessments:||
|Range Description:||This species is widely distributed in central and southern China (Shaanxi, Gansu and Henan, south to southeastern Tibet, Yunnan, Guangxi, Guangdong and Jiangxi; Yang et al. 2003, Zhou et al. 2004). It extends to the eastern Himalayas and into northeastern Viet Nam, and perhaps northern Lao PDR (there is unresolved historical information that this species also used to exist in Lao PDR; Chebinaud 1942, J.W. Duckworth pers. comm.).|
Native:China; Viet Nam
|Lower elevation limit (metres):||2000|
|Upper elevation limit (metres):||3800|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||Estimating population size or trend for Musk Deer is very difficult, and has rarely been done satisfactorily. Population estimates over large-scale areas are subject to considerable uncertainty (and this is exacerbated in China by uncertainty over taxonomy). The population in China was guessed at over one million in the 1960s; in 1978-1980 at less than 600,000; and in 1992 at 100,000 to 200,000 in 1992 (Sheng 1998). However, the basis for these estimates is unclear, though the strong declining trend is likely to be correct. In the late 1990s, the population in Viet Nam was estimated at 200, but it is now very rare (Do Tuoc pers. comm.).|
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||This species inhabits coniferous or broad-leaved forests, or mixed forests and shrublands at high elevations (2,000-3,800 m asl). In Viet Nam it is found in karst habitats (J.W. Duckworth pers. comm.). Animals are most active between dusk and dawn, alternately resting and feeding. Forest Musk Deer eat leaves, grasses, moss, lichens, shoots and twigs. These animals are shy, sedentary and remain within a defined home range throughout the year. Males utilize their large musk gland to defend their territory and attract mates. When alarmed they make great leaps with wild changes of direction. They can adroitly jump into trees to forage. Their main predators include leopard, marten, fox, wolf, lynx and especially humans. Gestation lasts 6.5 months, after which one or two young are born. During the first two months, the young deer lie hidden in secluded areas, independent of their mothers except at feeding times. They are weaned within three to four months and reach sexual maturity by 24 months. Animals may live up to 20 years. Home ranges of M. berezovskii were reported to be five to 10 hectares in China by Sheng and Liu (2007).|
|Generation Length (years):||7|
|Use and Trade:||
The musk produced by this genus of primitive deer is highly valued for its cosmetic and alleged pharmaceutical properties, and can fetch U.S. $45,000 per kilogram (2.2 pounds) on the international market. The Viet Namese population is heavily hunted by local people for medicinal use (Do Tuoc pers. comm.).
Captive breeding, primarily for commercial musk production, occurs in various places in China, and might have some conservation benefit.
|Major Threat(s):||The musk produced by this genus of primitive deer is highly valued for its cosmetic and alleged pharmaceutical properties, and can fetch U.S. $45,000 per kilogram (2.2 pounds) on the international market. Although this musk, produced in a gland of the males, can be extracted from live animals, most "musk-gatherers" kill the animals to remove the entire sac, which yields only about 25 grams (1/40 of a kilogram) of a brown waxy substance. Such poaching is relatively easy to accomplish and difficult to stop using only legal means (Harris 2007). Musk Deer appear to require dense vegetation, either in the form of intact forests or shrublands; thus excessive forest clearing or grazing can preclude Musk Deer from using such lands (Yang et al. 2003). The Viet Namese population is heavily hunted by local people for medicinal use, and is thought to persist in the country in only four localities (Do Tuoc pers. comm.).|
|Conservation Actions:||This species is listed in CITES Appendix II. It is on the 2015 China Red List as Critically Endangered (A1acd, B1ab(i,ii,iii)), and on the China Key List. Captive breeding, primarily for commercial musk production, occurs in various places in China, and might have some conservation benefit. However, to date, there is little evidence that the availability of musk from captive-bred animals has had a positive conservation impact in terms of reducing poaching pressure (Parry-Jones and Wu 2001, Green et al. 2007, Harris 2007).|
Cheminaud, G. 1942. Mes Chasses au Laos, volume 2. Payot, Paris, France.
Green, M.J.B., Taylor, P.M., Xu, H.F., Yin, F. and Lee, S.K.H. 2007. Part of the Solution or Part of the Problem? Assessing the Role of Captive Breeding for Conservation of Wild Populations of Animals Used in Traditional Chinese Medicine. Traffic East Asia, Hong Kong.
Groves, C.P., Yingxiang, W. and Grubb, P. 1995. Taxonomy of Musk-Deer, Genus Moschus (Moschidae, Mammalia). Acta Theriologica Sinica 15(3): 181-197.
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Wang, Y.X., Ma, S.L. and Li, C.Y. 1993. The taxonomy distribution and status of forest musk deer in China. In: O. Ohtaishi and H.L. Sheng (eds), Deer of China, Biology and Management, pp. 22-30. Elsevier, Amsterdam.
Wemmer, C. 1998. Deer Status Survey and Conservation Action Plan. IUCN, Gland, Switzerland and Cambridge, UK.
Yang, Q.S., Meng, X.X., Xia, L. and Lin Feng, Z.J. 2003. Conservation status and causes of decline of musk deer (Moschus spp.) in China. Biological Conservation 109: 333-342.
Zhou, Y.J., Meng, X.X., Feng, J.C., Yang, Q.S., Feng, Z.J., Xia, L. and Bartoš, L. 2004. Review of the distribution, status, and conservation of musk deer in China. Folia Zoologica 53: 129-140.
|Citation:||Wang, Y. & Harris, R. 2015. Moschus berezovskii. The IUCN Red List of Threatened Species 2015: e.T13894A61976926. . Downloaded on 24 June 2016.|
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