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Wikramanayake, E. D. (1995). Recommendations for Conservation Management of Jigme Dorji National Park.
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Schaller, G. B. (1971). Imperiled phantom of Asian peaks. National Geographic, 140, 702–707.
Abstract: Brief description of succssful baiting, with a domestic goat and photographing a wild snow leopard in Northern Pakistan.
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Ahmad, A. (1994). Protection of Snow Leopards through Grazier Communities:Some Examples from WWF-Pakistan's Projects in the Northern Areas. In J.L.Fox, & D.Jizeng (Eds.), (pp. 265–272). Usa: International Snow Leopard Trust.
Abstract: Snow leopards occur near the snow line in northern Pakistan in the districts of Swat, Dir and Chitral of the Northwest Frontier Province (NWFP), Muzaffarabad district in Azad Kashmir and Gilgit and Baltistan districts in the Northern Areas. Although a number of protected areas are present in the form of national parks, wildlife sanctuaries and game reserves (Table 1) where legal protection is available to all wildlife species, including snow leopards, the status of this endangered species is not improving satisfactorily. The reasons are many and range from direct persecution by livestock owners to the less than strict management of protected areas.
Because of remote and inaccessible locations and lack of proper communication with local communities, government officials and nongovernmental organizations (NGOs) concerned with conservation find it difficult to obtain statistics on mortality of snow leopards. However, the killing of snow leopards is not uncommon. Because of the close and long-term association between local villagers and snow leopards, it is only through the support and cooperation of these peoples that protection of this endangered species can be assured against most of the existing threats. The effects of such cooperation has been clearly shown through some of the conservation projects of World Wildlife Fund (WWF) – Pakistan. Details of such projects and certain lessons that can be learned from these and similar projects are discussed in this paper.
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Green, M. J. B., & Zhimbiev, B. (1997). Transboundary Protected Areas and Snow Leopard Conservation. In R.Jackson and A.Ahmad (Ed.), (pp. 194–202). Lahore, Pakistan: Islt.
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Freeman, H. (1988). Resolutions Conservation of Snow Leopard, Fifth International Snow Leopard Symposium. (pp. 267–269). Usa.
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Villarrubia, C., & Jackson, R. (1994). Snow Leopard Conservation on a Regional Basis: Elements in Planning Protected Areas. In J.L.Fox, & D.Jizeng (Eds.), (pp. 253–263). Usa: Islt.
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Anonymous. Indian Wildlife Protection Act.
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Yanfa, L. (1994). Snow leopard distribution, purchase locations and conservation in Qinghai Province, China. In J.L.Fox, & D.Jizeng (Eds.), (pp. 65–72). Usa: Islt.
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Taber, R. (1988). Long Term Research in Snow Leopard Conservation. In H.Freeman (Ed.), (pp. 255–259). India: International Snow Leopard Trust and Wildlife Institute of India.
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Mishra, C., & Rawat, G. S. (1998). Livestock grazing and Biodiversity Conservation: Comments on Saberwal. Conservation Biology, 12, 25–32.
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Allen, P. (2002). Conservation Increases Crafts Income (Vol. Winter, 2002).
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Ryan, J. A., Roudebush, P., & Shores, J. (1990). Laryngeal obstruction associated with cuterebrosis in a snow leopard (Felis-uncia). Journal of Zoo and Wildlife Medicine, 21(3), 346–352.
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Jackson, R. M., Ahlborn, G., Gurung, M., & Ale, S. (1996). Reducing livestock depredation losses in the Nepalese Himalaya. Proc.Vertebr.Pest Conf, 17, 241–247.
Abstract: The authors investigated livestock depredation patterns of snow leopards on the northern slopes of the Himalayans near the villages of Manang and Khangshar, Nepal. Information is discussed on the relationships among livestock loss, endangered species management, public relations/conservation issues, and cooperative efforts among institutions involved in the decision making process. A plan is devised for alleviating livestock loss and protecting endangered species in the area. pcp
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Machado, C., Brown, P., & Turner, R. (1984). Dental crown restorations on a snow leopard. Journal Of Zoo Animal Medicine, 15(4), 146–150.
Abstract: In the spring of 1983 the San Francisco Zoo received a female snow leopard (Panthera uncia) as part of an exotic animal exchange program with the People's Republic of China. Upon examination, it was found that this nine-yea old, seventy-five pound, wild-trapped animal had sustained considerable dental injuries, including fractures of all maxillary and mandibular anterior teeth. The purpose of this paper is to describe the dental procedures undertaken to restore the physiological function of all four canines.
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Rawat, G. S., Pandey, S., & Panwar, H. S. (1994). Eco-development and management needs for snow leopard conservation in Himalayan Protected Areas. In J.L.Fox, & D.Jizeng (Eds.), (pp. 297–303). Usa: Islt.
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Xinchun, M. (1994). Distribution in the wild and the captive raising of snow leopards in Xinjiang, China. In J.L.Fox, & D.Jizeng (Eds.), (pp. 157–162). Usa: Islt.
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Blomqvist, L. (1980). Distribution and Status of the Snow Leopard (Uncia uncia). Tiger Paper, Vii(4), 115–120.
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International Snow Leopard Trust. (1999). Snow Leopard News Summer/ Fall 1999. Seattle, WA: Islt.
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Grachev, U. A., & Fedosenko, A. K. (1991). Distribution and Numbers of Snow Leopard in Kazakhstan (Vol. ix). Seattle: Islt.
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Samant S.S., Dhar U., & Rawal R.S. (1998). Biodiversity status of a protected area in West Himalaya: Askot Wildlife Sanctuary. International Journal Of Sustainable Development And World Ecology, 5(3), 194–203.
Abstract: Biodiversity of a protected area of West Himalaya (Askot Wildlife Sanctuary) was studied and analysed for landscape, faunal and floral diversity. The forest and pasture land, ideal habitats for the flora and fauna, covered nearly 52% and 12%, respectively, of total reported area. Among the fauna Himalayan musk deer (Moschus chrysogaster), thar (Himitragus jemlahicus), snow leopard (Panthera uncia), koklas (Pucrassia macrolophas), monal (Lophophorus impejanus) and snow cock (Tetragalus tibetanus) are threatened species. Plant diversity is represented by 1262 species of vascular plants (Angiosperm 1112, Gymnosperm 7, Pteridophytes 143 taxa). Diversity of the species within families, genera, habitats, communities and along vertical gradient zone was analysed. Maximum diversity existed in the family Orchidaceae (120 taxa), genera Polystichum (13 taxa), altitude zone (1001-2000 m; 860 taxa), habitat (forest; 623 taxa) and community (Banj oak: 92 taxa). Seventy-one families were found to be monotypic. Species were further analysed for ethnobotanical use (medicine: 70, edible: 55, fodder: 115, fuel: 31, house building: 13 etc.), domesticated diversity (crops: 19, vegetables: 26, fruits: 16),agroforestry or marginal, threatened and endemic diversity. Similarity in species composition within the habitats indicated maximum similarity in areas of shrubberies and alpine meadows/slopes (71.65%) and exposed open/grassy slopes and shady moist places (47.32%). 432 (34.2%) taxa are native to Indian Himalaya of which 24 are endemic and 235 are near endemics. 65.8% of taxa are represented in the neighbouring areas and other regions of the globe. Ten taxa occurring in the Sanctuary have been already recorded in the Red Data Book of Indian Plants. Conservation and management of species is focused.
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Gruisen, J. V. (1993). Interaction Between Wild Dogs and Snow Leopards in Ladakh (Vol. xi). Seattle: Islt.
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Mishra, C. (2000). Socio-economic transition and wildlife conservation in the Indian Trans-Himalaya. Journal of the Bombay Natural History Society, 97(1), 25–32.
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Hol, E. H., Marden, T. B., & Roelke, M. E. (1994). The importance of ecotoxicological research in management of the snow leopard: lessons learned from the Florida panther. In J.L.Fox and D.Jizeng (Ed.), (pp. 113–125). Usa: Islt.
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Hol, E. H., & Marden, T. (1994). Methods for Sampling and Analysis to establish potential exposure of wildlife to persistent contaminants in remote areas. In J.L.Fox, & D.Jizeng (Eds.), (pp. 279–287). Usa: Islt.
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Woodroffe, R., & Ginsberg, J. R. (1998). Edge effects and the extinction of populations inside protected areas. Science Washington D.C., 280(5372), 2126–2128.
Abstract: Theory predicts that small populations may be driven to extinction by random fluctuations in demography and loss of genetic diversity through drift. However, population size is a poor predictor of extinction in large carnivores inhabiting protected areas. Conflict with people on reserve borders is the major cause of mortality in such populations, so that border areas represent population sinks. The species most likely to disappear from small reserves are those that range widely-and are therefore most exposed to threats on reserve borders-irrespective of population size. Conservation efforts that combat only stochastic processes are therefore unlikely to avert extinction.
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