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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Chundawat, R. S., & Qureshi, Q. (1999). Planning Wildlife Conservation in Leh and Kargil Districts of Ladakh, Jammu and Kashmir. Dehradun, India.
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Wangchuk, R., & Jackson, R. (2009). A Community-based Approach to Mitigating Livestock-Wildlife Conflict in Ladakh, India.
Abstract: Livestock depredation by snow leopard and wolf is widespread across the Himalayan region (Jackson et al. 1996, Jackson and Wangchuk 2001; Mishra 1997, Oli et al 1994). For example, in India's Kibber Wildlife Sanctuary, Mishra (1997) reported losses amounting to 18% of the livestock holdings and valued at about US $138 per household. The villagers claimed predation rates increased after establishment of the sanctuary, but
surveys indicated a dramatic increase in livestock numbers accompanying changes in animal husbandry systems (Mishra 2000).
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Jackson, R. (2000). Community Participation: Tools and Examples. (pp. 1–9). Management Planning Workshop for the Trans-Himalayan Protected Areas, 25-29 August, 2000, Leh, Ladak.
Abstract: In response to dwindling wildlife populations and habitat, governments established national parks and protected areas, often with little input from people living in the immediate area. In some cases communities were relocated, but in most they are left to pursue traditional agricultural and pastoral livelihoods under a new set of rules. Important questions of land tenure remained unresolved, with a “fences and fines” approach to protected area management (Stolton and Dudley 1999).
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Jain, N., Wangchuk, R., & Jackson, R. (2003). An Assessment of CBT and Homestay Sites in Spiti District, Himachal Pradesh.
Abstract: The survey described in this report builds upon prior CBT activities undertaken by The Mountain Institute (TMI) in partnership with the Snow Leopard Conservancy (SLC) in Ladakh, supported by a grant from UNESCO (with co-financing from SLC). Under the evolving concept of “Himalayan Homestays”, initially developed and tested in Ladakh, it is proposed that activities be expanded to selected states in India in a strategic and effective way. Himalayan Homestays are part of a larger integrated program to link snow leopard conservation with local livelihoods in Asia.
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Jackson, R., Roe, J., Wangchuk, R., & Hunter, D. (2005). Camera-Trapping of Snow Leopards. Cat News, 42(Spring), 19–21.
Abstract: Solitary felids like tigers and snow leopards are notoriously difficult to enumerate, and indirect techniques like pugmark surveys often produce ambiguous information that is difficult to interpret because many factors influence marking behavior and frequency (Ahlborn & Jackson 1988). Considering the snow leopard's rugged habitat, it is not surprising then that information on its current status and occupied range is very limited. We adapted the camera-trapping techniques pioneered by Ullas Karanth and his associates for counting Bengal tigers to the census taking of snow leopards in the Rumbak watershed of the India's Hemis High Altitude National Park (HNP), located in Ladakh near Leh (76ø 50' to 77ø 45' East; 33ø 15' to 34ø 20'North).
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Panwar, H. S., Fox, J. L., Sinha, S. P., & Chundawat, R. S. (1986). Ecology of the Snow Loepard and Associated Prey in Central Ladakh.
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Mallon, D. (1984). The snow leopard in Ladakh. International Pedigree Book of Snow Leopards, 4, 23–37.
Abstract: Reports on 1 summer survey and four winter surveys covering some 3100 km in Ladakh, India. Reports on snow leopard sign commonly found, distribution, prey, attacks on livestock and peoples reaction, mortality factors and conservation status. Suggest recomendations for preventing unnecessary killing of snow leopards and estimates population of 100 to 200 snow leopards in Ladakh
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Mallon, D. (1993). Snow Leopard in Kanji Wildlife Reserve, Ladakh (Vol. xi). Seattle: Islt.
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Jackson, R., Wangchuk, R., & Hillard, D. (2002). Grassroots Measures to Protect the Endangered Snow Leopard from Herder Retribution: Lessons Learned from Predator-Proofing Corrals in Ladahh.. Islt: Islt.
Abstract: Livestock depredation is an increasingly contentious issue across the range of the
endangered snow leopard (Uncia uncia). Depredation is most severe in or near protected areas
offering core habitat for this cat. “Surplus killing,” in which as many as 100 sheep and goats have
been killed in a single night, inevitably results in attempts at retaliatory killing of predators by
herders suffering significant loss. Ironically, such predation by snow leopard, wolf, or lynx can be
avoided by adequately predator-proofing nighttime enclosures. Predation on the open range is far
more difficult to address, but may be reduced to acceptable levels through improved day-time
guarding of livestock, educating herders on the importance of protecting the predator's natural prey
base, and by providing economic incentives to help offset unavoidable loss.
This paper describes community-based initiatives being undertaken in India's Hemis National Park
aimed at predator-proofing livestock corrals and encouraging local herders to become more effective
stewards of the snow leopard, its prey and habitat. A highly participatory, 4-step process known as
Appreciative Participatory Planning and Action (APPA) provides the primary mechanism for
assisting communities to develop Action Plans to reduce livestock depredation losses, increase
household incomes, and strengthen environmental stewardship. Herders are informed about the
Snow Leopard Stewardship program and conditions for a successful outcome. The team, comprised
of local people, NGO staff, facilitators and government officials, first identifies the root causes for
depredation (Discovery). Under the next phase, Dreaming, participants envision how their village
might appear if depredation losses were reduced to acceptable levels, household incomes increased,
and snow leopards fully protected. This provides a good basis upon which to collaboratively devise
actions for addressing the community's concerns (Design). Delivery involves implementing actions
under the overall Action Plan, as well as specific measures that can be acted upon immediately. The
community is encouraged to use simple but realistic indicators for monitoring the project's
effectiveness.
In Lessons Learned to Date, we highlight the importance of providing meaningful community
involvement from inception through project implementation and monitoring. The use of _APPA
_greatly increases ownership, communal empowerment and self-reliance, and local people's
willingness to protect wildlife. The Snow Leopard Conservancy believes that the most effective
conservation actions will be contingent upon (1) establishing direct linkages with biodiversity
protection; (2) ensuring reciprocal co-financing and commensurate responsibility from the
community; (3) encouraging full participation from all stakeholders irrespective of their gender, age
or economic status; and (4) ensuring regular monitoring and evaluation under an agreed-to Action
Plan that sets forth the responsibilities, contributions and obligations of each partner.
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