Harris, R. B. (1994). Dealing with uncertainty in counts of mountain ungulates. In J.L.Fox, & D. Jizeng (Eds.), (pp. 105–111). Usa: Islt.
|
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.
|
Taryannikov, V. I. (1986). Distribution, biology and current state of the number of the rare predatory mammals in W. Gissar. The Ecology, Protection, and Acclimatization of Vertebrates in Uzbekistan. Tashkent.
|
Koshkarev, E. (1994). Evaluation of the presence of snow leopard and ibex in Southern Siberia. In J.Fox, & D.Jizeng (Eds.), (pp. 17–27). Seattle/USA: Islt.
|
International Snow Leopard Trust. (1993). First SLIMS Workshop Held in China (Vol. xi). Seattle: Islt.
|
Abzalov A.A. (1974). Game management development.
Abstract: An issue of wildlife conservation in game preserves, forestries, and sanctuaries is discussed. In some regions of Uzbekistan there are various protected wildlife areas preserving unique and game species: marchor in the Kugitan hunting farm, Bukhara deer the Bukhara region, bear and snow leopard, argali, ibex, wild-boars, snow-cock, partridge, eagle, etc. in the Miraki hunting farm, pheasants in the Karadara forestry. To restore and upgrade the game management level in the country it is required to properly create game preserves, enlarge reproduction activity, strictly follow rules and terms of hunting and cultivate careful and solicitous attitude to wildlife and its resources in all hunters.
|
Pavlinov I.Ya. (2002). Genus irbis (Uncia Gray, 1854), irbis (Uncia uncia Schreber, 1776). Terrain animals of Russia. Reference book identifier.
Abstract: It provides brief characteristics of terrain mammals in Russia: taxonomy, synonyms, principle features, distribution, habitat, biological features. Snow leopard is distributed in the mountains (from 800 to 5,000 m above sea level) of Central Asia Himalayas, Tibet, Pamir, Tien-Shan; in Russia the Altai, Tuva, southern Transbaikalia.
|
Aristov A.A. (2001). Genus Irbises Uncia Gray, 1854. Irbis or snow leopard Uncia uncia (Schreber, 1775).
Abstract: An identification table for genus and species of mammals of Russia and adjacent areas is given. The taxonomy, morphology, distribution and life history of carnivores are described. The features of genus Uncia and species Uncia uncia, geographical variability, distribution, biology and value are described in detail.
|
Geptner V.G. (1972). Genus snow leopard or irbis (Vol. Vol. 2, Part 2.).
Abstract: It describes genus and species features of snow leopard such as appearance, skull, sizes, phylogenetic links, distribution, geographic variability, biology including number, habitat, refuges, activity in daylight and night, behavioral patterns, reproduction, enemies and rivals, and practical use of the species.
|
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.
|