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Fox, J., Nurbu, C., Bhatt, S., & Chandola, A. (1994). Wildlife conservation and land-use changes in the Transhimalayan region of Ladakh, India (Vol. 14).
Abstract: Changes in economy and land use are under way in the Indian Transhimalayan region of Ladakh, creating both negative and positive prospects for wildlife conservation in this sparsely populations and previously remote area. New livestock breeds, irrigation developments, farming practices, foreign tourists, and a large military presence are changing the way people view and use the mountainous land that surrounds them. With only 0.3% of the land currently arable, changes in wildlife and natural resource conservation are most apparent on Ladakh's extensive rangelands which are apparently undergoing a redistribution of use associated with social changes and recently introduced animal husbandry and farming practices. International endangered species such as the snow leopard, several wild ungulates, and the black-necked crane provide special incentive for conservation efforts in what are some of the best remaining natural areas in the mountainous regions to the north of the Himalayan crest. The success of newly created protected areas for wildlife conservation in Ladakh rests on an understanding of the effects of various development directions, a commitment to environmentally sensitive development amid the many competing demands on Ladakh's natural resources, conservation laws appropriate to human needs, and a clear recognition that solutions can be neither directly adaptable from other mountainous areas nor even widely applicable across the Himalayan region.
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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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Ahmad, A. (1997). Community-Based Natural Resources Management in Northern Pakistan. In R.Jackson and A.Ahmad (Ed.), (pp. 148–154). Lahore, Pakistan: Islt.
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Wikramanayake, E. D. (1995). Recommendations for Conservation Management of Jigme Dorji National Park.
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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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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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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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