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International Snow Leopard Trust. (1998). ISLT Hires Snow Leopard Conservationist in India.
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Jackson, R. (1992). SCC Plan for snow leopard.
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Fox, J. (1989). Snow Leopard. Panthera uncia Schreber 1776.
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Mallon, D. (1987). Snow Leopards in Northern Hunza.
Abstract: In fall 1987 an expedition from Operation Raleigh went to Hunza in Pakistan. In promoting expeditions for young people from many countries. the London-based organization aims to carry out scientific. community. and adventure projects all over the world. One objective of the 40-strong team based at Passu in northern India was a preliminary survey of the snow leopard and large ungulates.
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Hillard, D. (1986). Field report form the Himala V an Snow Leopard Project: Survey In Hongu Valley After participating in the Fifth International Snow Leopard Symposium in Srinagar.1–3.
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Abdusaljamov I.A., M. S. R. (2001). Conservation strategy of rare and endanger vertebrate species of Tajikistan republic. Bulletin of Academy of Sciences of Republic Tajikistan, 2(143), 40–48.
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Janeč, & ka, J. E., Munkhtsog, B., Jackson, R.M., Naranbaatar, G., Mallon, D.P. & Murphy, W.J. (2011). Comparison of noninvasive genetic and camera-trapping techniques for surveying snow leopards. Journal of Mammalogy, 92(4), 771–783.
Abstract: The endangered snow leopard (Panthera uncia) is widely but sparsely distributed throughout the mountainous regions of central Asia. Detailed information on the status and abundance of the snow leopard is limited because of the logistical challenges faced when working in the rugged terrain it occupies, along with its secretive nature. Camera-trapping and noninvasive genetic techniques have been used successfully to survey this felid. We compared noninvasive genetic and camera-trapping snow leopard surveys in the Gobi Desert of Mongolia. We collected 180 putative snow leopard scats from 3 sites during an 8-day period along 37.74 km of transects. We then conducted a 65-day photographic survey at 1 of these sites, approximately 2 months after scat collection. In the site where both techniques were used noninvasive genetics detected 5 individuals in only 2 days of fieldwork compared to 7 individuals observed in the 65-day camera-trapping session. Estimates of population size from noninvasive genetics ranged between 16 and 19 snow leopards in the 314.3-km2 area surveyed, yielding densities of 4.9–5.9 individuals/100 km2. In comparison, the population estimate from the 65-day photographic survey was 4 individuals (adults only) within the 264-km2 area, for a density estimate of 1.5 snow leopards/100 km2. Higher density estimates from the noninvasive genetic survey were due partly to an inability to determine age and exclude subadults, reduced spatial distribution of sampling points as a consequence of collecting scats along linear transects, and deposition of scats by multiple snow leopards on common sites. Resulting differences could inflate abundance estimated from noninvasive genetic surveys and prevent direct comparison of densities derived from the 2 approaches unless appropriate adjustments are made to the study design.
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Kuznetsov, B. A. (1948). Province of mountains of Central Asia.
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WWF Russia & WWF Mongolia Programme Office. (2011). Altai-Sayan Ecoregion WWF Newsletter April-June 2011 (Vol. April-June).
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Kanderian, N., Lawson, D., Zahler, P. (2011). Current status of wildlife and conservation in Afghanistan. International Journal of Environmental Studies, 68(3), 281–298.
Abstract: Afghanistan’s position in latitude, geography and at the intersection of three biogeographic realms has resulted in a surprising biodiversity. Its wildlife includes species such as the snow leopard, Asiatic black bear, Marco Polo sheep, markhor and greater flamingo. Principal threats include high levels of deforestation, land encroachment and hunting for food and trade. Continuing security issues have also made it difficult to monitor species abundance and population trends. Over the last decade, however, survey efforts have provided the first collection of species and habitat data since the late 1970s. Initial findings are enabling the Government and rural communities to begin implementing important conservation measures. This process has included policy development and protected area planning, promoting alternative livelihoods and responsible community management, and continuing research into the status of biodiversity in the field.
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