|Scientific Name:||Rhinopithecus strykeri|
|Species Authority:||Geissmann, Ngwe Lwin, Saw Soe Aung, Thet Naing Aung, Zin Myo Aung, Tony Htin Hla, Grindley & Momberg, 2011|
|Taxonomic Notes:||This is a new species of Snub-nosed Monkey from the high altitudes of northeastern Kachin state, northeastern Myanmar. Descriptions are based on a skin and skulls of four specimens obtained from local hunters. The new species is geographically isolated from other Snub-nosed Monkeys and separated from them by two major barriers - the Mekong and the Salween (Thanlwin) rivers.|
|Red List Category & Criteria:||Critically Endangered A4cd ver 3.1|
|Assessor(s):||Geissmann, T., Momberg, F. & Whitten, T.|
|Reviewer(s):||Schwitzer, C. & Molur, S.|
The species is listed as Critically Endangered under criterion A4cd. Geissmann et al. (2011) estimated a three-generation period for this species of 18 years, and the time-frame used for this assessment applies to the past three years and is projected forwards for the next fifteen years. The total population size was estimated between 260 and 330 individuals. Based on the interviews with hunters (Momberg et al. 2010), at least 13 Burmese Snub-nosed Monkeys were hunted during 2009. If this figure is extrapolated to three-generation spans (at least 18 years), the rate of loss would be 234 monkeys, or 90% of the conservatively estimated current total population of 260 individuals. Under this scenario, in order to keep hunting success stable with decreasing supply, hunting effort would have to increase. All the evidence on threats indicates that hunting pressure (directed and undirected) is likely to increase considerably in the next few years as new dam construction and logging roads invade the distribution area of this newly discovered Snub-nosed Monkey. The 90% population reduction scenario also implies that will be very little to no population growth, although this may be unlikely, it is very probable that there will be increasingly less recruitment over the next fifteen years as the population declines. Hence an estimated and projected population reduction of more than 80% over the three generation period seems perfectly reasonable for this highly threatened species.
|Range Description:||The trapping locality of the holotype was determined as 26.431011°N, 98.388941°E (elevation 2,815 m) in the Maw River area, northeastern Kachin state, northeastern Myanmar. Preliminary surveys and notes on habitat associations indicate that the range of the new species encompasses the mountain forests in the watershed area of the Maw River, a tributary to the N'mai Hka River, and forests across the range to the east above the village of Chichitago. The species therefore appears to be limited in distribution to a small area of the Salween-N'mai Hka divide in northeastern Kachin state, northeastern Myanmar. The coordinates of the distribution area are 26.31°–26.51°N and 98.34°–98.61°E.|
Native:Myanmar (Myanmar (mainland))
|Range Map:||Click here to open the map viewer and explore range.|
Geissmann et al. (2011) estimated that there are approximately three to four groups of Burmese Snub-nosed Monkeys, which occur in three distinct parts of the distribution area around Maw River. The first group, distributed north of the Maw River, contains approximately 60-80 individuals; the second group, south of the river has about 80-100 individuals; and a group of about 150 animals appears at the foothills of the snow-capped mountains above the Chichitago village. The total population size was estimated at 260-330 individuals. The generation length of Snub-nosed Monkeys is unknown, however, Geissmann et al. (2011) used the age at first reproduction as a minimum estimate of generation length. In other species of Snub-nosed Monkeys, the average age at first reproduction is 4–6 years in females and 6.5–7 years in males (Li et al. 2003; Liang et al. 2000; Quan and Xie 2002, cited in Liu et al. 2009; Zou 2002, cited in Cui et al. 2008). This gives an average of about six years for the age at first reproduction.
After two years of field work in this area the only direct encounters with this species were by local support staff (twice) and not by any scientists and the presence of the species in the wild was only confirmed through camera traps (one group of eleven including three mothers with infants, and two individual animals on three camera traps in total) over a nine month period (F. Momberg pers. comm. 2012). Given the lack of direct evidence, the population size estimates given above are treated as being highly uncertain and as a result, these numbers are not used in the assessment of this species to see if it would qualify as Critically Endangered under criterion C. The lower population estimate of 260 is very close to the required threshold of less than 250 mature individuals; the species would most certainly qualify as Endangered under criterion C1 and C2.
|Habitat and Ecology:||The distribution area is mountainous, and slopes are very steep in most places. The main forest types in the range of the Snub-nosed Monkeys are cool temperate rain forest and mixed temperate forest. Silver fir forest occurs at elevations of 2,745-3,660 m (conifer zone). There is no information how high up the mountains the monkeys go, but the highest mountain in this range is 3,660 m. According to local hunters, Snub-nosed Monkeys spend the summer (i.e. the snow-free times from May to October) mostly at higher altitudes, in mixed temperate forests and conifer forests. In winter, however, when snowfall probably restricts the availability of food, the monkeys descend to lower elevations and may be found closer to villages.|
|Use and Trade:||The species is hunted for its bones and head (skull and brains) presumably for medicinal purposes. The bones and heads are sold to Chinese workers at the nearby road construction and logging camps, as well as to wildlife traders in Kangfang, the nearest town on the Chinese border (T. Geissmann pers. comm. 2012). It is also hunted for its fur. A bag made out of the skin of a juvenile Snub-nosed Monkey was obtained from a hunter from Htantan on 23 February 2010.|
Snub-nosed Monkeys are threatened by direct and indirect hunting pressures. Animals are hunted and trapped for their bones and heads, but most often monkeys are unintentionally trapped in iron traps that are set to trap deer or wild pigs to supply the local bush meat trade (this has been confirmed by local hunters and there is camera trap evidence of the monkeys travelling on the ground where traps have been set) (F. Momberg pers. comm. 2012). Already with the still limited construction work camps, commercial bush meat demand has increased sharply over the last two years (2010-2011) and is set to accelerate (F. Momberg pers. comm. 2012). Monkeys may also be caught in traps set for bears (T. Geissmann pers. comm. 2012).
Habitat degradation, due to the creation of roads and other infrastructure is rapidly becoming a major threat. Logging roads have now been built into all the areas occupied by this species since 2009 (some are within 200 m of the camera traps) (F. Momberg pers. comm. 2012). With the increased access, the influx of Chinese workers to the area as part of the logging and dam building operations is accelerating and it is expected that when the dams reach the full construction stage there will be at least 10,000 workers employed in this area (F. Momberg pers. comm. 2012).
Habitat loss due the impacts of logging is very serious due to large scale mechanical logging (blasting of logging roads, use of heavy equipment and winches, reaching ridges and even peaks) taking place, especially as the largest part of the range area is conifer forest and during the snow-covered winter months the Snub-nosed Monkeys (just as R. bieti) depend on lichens for food (F. Momberg pers. comm. 2012). As the logging is effecting most mature conifer trees, food sources especially in winter are becoming scarce. The logging practices are causing serious destruction because logging takes place at high altitudes and even on slopes with more than 70 degrees slope inclination (these areas are accessed using winches and roads are blasted through cliffs). Land slides are becoming increasingly common as a result of the loss of tree cover. The lower mountain broad leaf forest is also impacted by logging (targeting hardwoods) and landslides caused by logging roads. Shifting cultivation reaches from the N'mai Hka river valley up to 2,000 meters, flooding following dam construction will displace shifting cultivation areas in the valley bottom to higher areas, increasing the pressures on the Snub-nosed Monkey habitat (F. Momberg pers. comm. 2012).
|Conservation Actions:||There are no direct conservation measures in place for this species. The area is not yet under Myanmar government control (it is within the ceasefire area with the National Democratic Army of Kachin), there are no border controls, no presence of enforcement agencies, and no rule of law. It is not known if the species is present within any protected areas. There is an urgent need to maintain areas of suitable forest within the range of this species.|
Cui, L.W., Huo, S., Zhong, T., Xiang, Z.F., Xiao, W. and Quan, R.C. 2008. Social organization of black-and-white snub-nosed monkeys (Rhinopithecus bieti) at Deqin, China. American Journal of Primatology 70: 169-174.
Geissmann, T., Ngwe Lwin, Saw Soe Aung, Thet Naing Aung, Zin Myo Aung, Htin Hla, Grindley, M. and Momberg, F. 2011. A new species of Snub-Nosed Monkey, genus Rhinopithecus Milne-Edwards, 1872 (Primates, Colobinae), from northern Kachin state, northeastern Myanmar. American Journal of Primatology 73: 96-107.
IUCN. 2012. IUCN Red List of Threatened Species (ver. 2012.1). Available at: http://www.iucnredlist.org. (Accessed: 19 June 2012).
Liang, B., Zhang, S.Y. and Wang, L.X. 2000. Development of sexual morphology, physiology and behaviour in Sichuan golden monkeys, Rhinopithecus roxellana.. Folia Primatologica 71: 413-416.
Li, H., Meng, S.J., Men, Z.M., Fu Y.X. and Zhang, Y.P. 2003. Genetic diversity and population history of golden monkeys (Rhinopithecus roxellana). Genetics 164: 269–275.
Liu, Z., Ren, B., Wu, R., Zhao, L., Hao, Y., Wang, B., Wei, F. Long, Y. and Li, M. 2009. The effect of landscape features on population genetic structure in Yunnan snub-nosed monkeys (Rhinopithecus bieti) implies an anthropogenic genetic discontinuity. . Molecular Ecology 18: 3831-3846.
Momberg, F., Lwin, N. and Geissmann, T. 2010. Report on a snubnosed monkey and biodiversity field survey, April 24–May 8, 2010. In: Yangon: Myanmar Primate Conservation Program (ed.).
|Citation:||Geissmann, T., Momberg, F. & Whitten, T. 2012. Rhinopithecus strykeri. The IUCN Red List of Threatened Species. Version 2015.2. <www.iucnredlist.org>. Downloaded on 31 July 2015.|