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Zhang, W., & Zhang, F. (2000). Beast of Prey. Harbin: North-eastern Forestry University Press.
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Primack, R. J. W. Z. (2000). A Primer of Conservation Biology. Beijing: China Forestry Publishing House.
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Bo, W. (2000). Snow Leopard Smuggling Aborted.
Abstract: Full Text:
Xining, China Daily, Jan. 31--Police have detained a man for trying to smuggle two dead snow leopards, an endangered species under State protection, through the Xining Railway Station in Northwest China's Qinghai Province. Ma Deliang was stopped by police after he attempted to pass the butchered snow leopards off as beef at a shop in Sichuan Province. Ma later confessed that he bought the dead snow leopards at a local market and wanted to smuggle them to Deyang in Sichuan Province. Police also searched Ma's home and found dear heads, antlers and lynx and fox furs. Snow leopards live in highlands of altitudes between 3,000 to 6,000 metres above sea level. The population of the species has dwindled greatly since the 19th century.
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Joslin, J. O., Garner, M., Collins, D., Kamaka, E., Sinabaldi, K., Meleo, K., et al. (2000). Viral papilloma and squamous cell carcinomas in snow leopards (Uncia uncia). In 2000 Proceedings AAZV & IAAAM Joint Conference (pp. 155–158). AAZV & IAAAM Joint Conference.
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Du, L., & Ming, M. (2000). Wildlife in Xinjiang. Urumqi: Xinjiang Juvenile Publishing House.
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Harder, T., & Toropova, V. (2000). Snow leopard conservation in Kyrghyzstan (Kyrgyzstan) (A. Kovshar, Ed.). IUCN (The World Conservation Union) Newsletter. IUCN (The World Conservation Union).
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Heinen, J. T., & Mehta, J. (2000). Emerging issues in legal and procedural aspects of buffer zone management with case studies from Nepal. Journal of Environment and Development, , 45–67.
Abstract: Buffer zones have been used as part of larger integrated conservation development programs to provide the benefits of ecological buffering of protected areas and socioeconomic buffering of neighboring communities. The authors explore the legal and managerial development of buffer zones internationally and with the passage of a conservation amendment in Nepal. A review of Nepal's buffer zone policies and several ongoing projects shows that there are several potential inherent problems. As written, regulations tend to expand the authority of the state by imposing restrictions in populated areas formerly not under control of park officials. Some participatory rights are provided to citizens, but management authority largely remains top down from the standpoint of local users. The authors question whether the managerial and research capacities exist to monitor buffer zones for their effectiveness both for conservation and development purposes and make several recommendations to improve implementation.
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Jackson, R., Wangchuk, R. (2000). People-wildlife conflicts in the trans-Himalaya. (pp. 1–10).
Abstract: Wildlife-related crop and livestock damage is emerging as a leading source of conflict between local communities, protected areas and park managers throughout India and the Himalayan region (Kharel 1997, Mishra 1997, Saberwal et al. 1994 and Sekhar 1998). For example, a comprehensive household-level survey of herders living in Nepal’s Annapurna Conservation Area suggested that predation accounted for 63% of all livestock mortality over a 18-24 month period, mostly attributable to snow leopard (Jackson et al. 1996). Oli et al. (1994) reported the predation rate at 2.6% of the stockholding, with losses representing as much as 25% of the average household’s per capita income. Hardly surprisingly, most local people held strongly negative attitudes toward snow leopard and wolf. In the Kibber Wildlife Sanctuary in Lahaul-Spiti, Mishra (1997) reported that 18% of the livestock holding were killed over a 18 month period, amounting to 1.6 animals per household perannum, with an estimated total value of US $ 128 per family per year. Villages received compensationin only 28 of 131 reported cases. According to local residents, predation rates in the sanctuary had increased markedly since its establishment. Mishra (1997) attributes this to a dramatic increase in livestock numbers accompanying a shift rom subsistence to a more commercially-based animal husbandry pattern.
The purpose of this presentation is to provide an overview of livestock damage from wild carnivores and how protected area managers could best approach this contentious issue. The author uses Hemis National Park as a case study example, focusing on baseline information gathering, and past, current and proposed remedial actions for reducing losses and compensating livestock owners.
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McCarthy, T. (2000). Ecology and Conservation of Snow Leopards, Gobi Brown Bears, and Wild Bactrian Camels in Mongolia. Ph.D. thesis, University of Massachusetts, Amherst, .
Abstract: Snow leopard ecology, distribution and abundance in Mongolia were studied between 1993 and 1999. I placed VHF and satellite radio-collars on 4 snow leopards, 2 males and 2 females, to determine home ranges, habitat use, movements, and activity. Home ranges of snow leopards in Mongolia were substantially larger than reported elsewhere. Males ranged over 61 – 142 km2 and female 58 to 1,590 km2. Cats had crepuscular activity patterns with daily movements averaging 5.1 km. Intraspecific distances averaged 1.3 km for males to 7.8 km for males. Leopards selected moderately to very-broken habitat with slopes > 20o, in areas containing ibex. Leopard distribution and abundance was determined using sign surveys. Leopard range in Mongolia is approximately 103,000 km2 but cats are not uniformly distributed within that range. High-density areas include the eastern and central Transaltai Gobi and the northern Altai ranges. Relative leopard densities compared well with relative ibex densities on a regional basis. A snow leopard conservation plan was drafted for Mongolia that identifies problems and threats, and provides an action plan. Wild Bactrian camels occur in the Great Gobi National Park (GGNP) and are thought to be declining due to low recruitment. I surveyed camels by jeep and at oases, observing 142 (4.2% young) and 183 (5.3% young) in 1997 and 1998. Current range was estimated at 33,300 km2. Some winter and calving ranges were recently abandoned. Track sizes and tooth ages from skulls were used to assess demographics. A deterministic model was produced that predicts camel extinction within 25 to 50 years under current recruitment rates and population estimates. Gobi brown bears are endemic to Mongolia and may number less than 35. Three population isolates may occur. I collected genetic material from bears at oases using hair traps. Microsatellite analyses of nuclear DNA determined sixteen unique genotypes, only two of which occurred at more than one oases. Genetic diversity was very low with expected heterozygosity = 0.32, and alleles per locus = 2.3. Mitochondrial DNA sequences were compared to other clades of brown bear and found to fall outside of all known lineages.
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Jackson, R., & Fox, J. L. (2000). Report on Fifth Slims Training Workshop (Nepal) (Vol. xvii). Seattle: International Snow Leopard Trust.
Abstract: Nepal's snow leopards (Uncia uncia) are mostly found along the northern border with Tibet (China). The largest populations are in Dolpa, Mugu, Manang, and Myagdi Districts. Potential habitat totals about 30,000 square kilometers. Numbers are estimated at 300-500, but surveys are urgently needed to confirm this rough guess. Like elsewhere, the primary threats center on poaching, depletion of natural prey, livestock depredation and resultant retributive killing of snow leopards by herders, and the lack of public awareness and support for conserving snow leoaprds, especially among local herders.
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