Hussain, S. (2002). Nature and Human Nature: Conservation, Values and Snow Leopard.. Islt: Islt.
Abstract: The failure of top-down environmental conservation practices gave rise to the so-called
`Community Based Conservation' or CBC approach. CBC promises to achieve the dual goals of
conserving nature and improving peoples' livelihoods. CBC programs also aim to involve local
communities as active partners in conservation efforts, and to use traditional knowledge and
local values in management of resources (Adams & Hulme 2001; Agrawal & Gibson 1999).
There are variations between different CBC programs; however, the underlying rationale of the
approach, common to all programs, is that introducing or changing economic incentives into the
conservation calculus of local people will bring about the behavioural change necessary for
successful conservation (Kellert et al 2000). Thus, the major emphasis in CBC programs is
conserving nature based on its utilitarian value. Since utilitarian value is measured in terms of
economics, hence the emphasis of CBCs on economic incentives in promoting conservation.
Recent evaluation of the CBC approach has shown that while local people may have benefited in
economic terms from the use of nature, no tangible improvements in biodiversity conservation
have occurred (Kellert et al 2000; Terborgh 1999). The disappointing performance of CBC
programs, which promised so much and yet have failed in practice to deliver, has recently lead to
a resurgence of the protectionist approach, calling for a renewed separation between the
conservation and human development objectives (Redford & Sanderson 2000; Terborgh 1999;
Oats 1999). Others, however, believe that the CBC approach has enormous potential, and that a
return to protectionist strategies would be disastrous, like `reinventing the square wheel'
(Brechin 2001; Wilhusen 2001). It is crucial that the flaws in the CBC approach are remedied if
there is to be any hope of a conservation agenda that does not conflict with the needs, aspirations
and interests of local people, and that therefore has a chance of having a long term, sustainable
conservation outcome.
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Taber, R. D. (1988). Toward a Free-Living Snow Leopard Recovery Plan. In H.Freeman (Ed.), (261). Usa: ISLT and Wildlife Institute of India.
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Green, M. J. B. (1992). Nature Reserves of the Himalaya and the Mountains of Central Asia. New Delhi: IUCN, Cambridge and Oxford University Press.
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Gvozdev, E. V., & Aliev, S. J. (1978). Red Data Book of Kazakh SSR. Alma-Ata: Kainar Publishing House.
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Fox, J. L., & Freeman, H. (1984). An Internationally cooperative fiels study of the snow leopard in Northern India. In L.Blomqvist (Ed.), (Vol. 4, pp. 39–42). Helsinki, Finland: Leif Blomqvist and Helsinki Zoo.
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Yang, Q. S., & Feng, Z. J. (1998). Snow Leopards Uncia Uncia. (pp. 132–135). Beijing: Science Press.
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O'Brien, S. J. (2003). Tears of the Cheetah: And Other Tales from the Genetic Frontier. New York: Thomas Dunne Books/St. Martin's Press.
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Bowling, B. (2004). The Legal Status of Snow Leopards in Afghanistan. United Nations Environment Programme.
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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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Novikov, G. A. (1962). Carnivorous mammals of the fauna of the USSR. Ussr: Zool. Inst. Acad. Sci.
Abstract: Brief review of physical characteristics, (skull illustration) ecology and distribution
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