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Gurung, G. S. (2011). Enhancing herder's livelihoods and conserving the snow leopard in Nepal. Cat News, 55, 6.
Abstract: Loss of livestock to snow leopards Panthera Uncia is one of the primary concerns of subsistence herders' communities and one of the primary threats to conservation of this endsngered species throughout the alpine regions of the central Asia. Unless the relationship between snow leopards abd humans is better understood and appropriate strategies are applied, coexistence may not be sustainable. thus, to address this issue, WWF Nepal piloted a community-managed livestock insurance scheme in Ghunsa valley of Kangchenjunga Conservation Area simultaneously with various types of mitigation measures (i.e preventive and curative) We found significan advantages of the insurance scheme including that it is self-sustaining and locally managed thereby ensuring it is economically viable and effective in preventive retaliatory killing of snow leopards. The main strength of the insurance scheme is that it was designed and developed in close co-operation with the affected herders' communities. The communities start by designing a simple livestock insurance plan whereby owners contribute to a common fund that is later administered and managed at the local level, thus reducing likelihood of fraud. Benefit sharing of funds among subsistence herders' communities from income generating activities is on of the positive motivating tools for people towards snow leopards. Since initiated, snow leopard killings have gone from 1-3/year to 0/year for 3 years.
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Anwar, M., Jackson, R., Nadeem, M., Janecka, J., Hussain, S., Beg, M., Muhammad, G., and Qayyum, M. (2011). Food habits of the snow leopard Panthera uncia (Schreber, 1775) in Baltistan, Northern Pakistan. European Journal of Wildlife Research, (3 March), 1–7.
Abstract: The snow leopard (Panthera uncia) inhabits the high, remote mountains of Pakistan from where very little information is available on prey use of this species. Our study describes the food habits of the snow leopard in the Himalayas and Karakoram mountain ranges in Baltistan, Pakistan. Ninety-five putrid snow leopard scats were collected from four sites in Baltistan. Of these, 49 scats were genetically confirmed to have originated from snow leopards. The consumed prey was identified on the basis of morphological characteristics of hairs recovered from the scats. It was found that most of the biomass consumed (70%) was due to domestic livestock viz. sheep (23%), goat (16%), cattle (10%), yak (7%), and cattle–yak hybrids (14%). Only 30% of the biomass was due to wild species, namely Siberian ibex (21%), markhor (7%), and birds (2%). Heavy predation on domestic livestock appeared to be the likely cause of conflict with the local inhabitants. Conservation initiatives should focus on mitigating this conflict by minimizing livestock losses.
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Suryawanshi, K. (2011). An encounter in snow. FRONTLINE, 28(10).
Abstract: In the trans-Himalayan region, a conservation effort has reduced conflicts between snow leopards and pastoralists. Photographs & text by author.
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Shrestha, B., Kindlmann, P. (2011). Interactions between the Himalayan tahr, livestock and snow leopards in the Sagarmatha National Park. Himalayan Biodiversity in the Changing World, .
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Suryawanshi, K., K. (2011). Sunshine and the Shadow. Hornbill, (April-June), 34–37.
Abstract: Kulbhushansingh Suryawanshi shares an update on his blog which describes snow leopard sightings in Spiti, Himachal Pradesh, while studying the foraging behavior and eating habits of blue sheep (Pseudois nayaur).
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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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Simms, A., Moheb, Z., Salahudin, Ali, H., Ali, I. & Wood, T. (2011). Saving threatened species in Afghanistan: snow leopards in the Wakhan Corridor. International Journal of Environmental Studies, 68(3), 299–312.
Abstract: The Wakhan Corridor in northeast Afghanistan is an area known for relatively abundant wildlife and it appears to represent Afghanistan’s most important snow leopard landscape. The Wildlife Conservation Society (WCS) has been working in Wakhan since 2006. Recent camera trap surveys have documented the presence of snow leopards at 16 different locations in the landscape. These are the first camera trap records of snow leopards in Afghanistan. Threats to snow leopards in the region include the fur trade, retaliatory killing by shepherds and the capture of live animals for pets. WCS is developing an integrated management approach for this species, involving local governance, protection by a cadre of rangers, education, construction of predator-proof livestock corrals, a livestock insurance program, tourism and research activities. This management approach is expected to contribute significantly to the conservation of snow leopards and other wildlife species in the Wakhan.
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Trivedi, P. (2011). From Cashmere to Gowa. Journal of East China Normal University (Special Issue of Zoology)nbill, (April-June), 4–10.
Abstract: Story of research trip looking for Tibetan Gazelle (Procapra picticaudata) in its last stronghold in India – Kalak Tar Tar (KTT) plateau in the Hanle area of hangthang – the great Tibetan high altitude plain that stretches at its extreme south-western and southeastern edges into India in Ladakh and Sikkim respectively. Species is known locally as “gowa”.
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Ming, M., Munkhtsog, B., McCarthy, T., McCarthy, K. (2011). Monitor ing of Population Density of Snow Leopard in X injiang. Journal of Ecology and Rural Environment, 27(1), 79–83.
Abstract: The snow leopard (Uncia uncia) is a very rare species in China. The survey of traces of snow leopard in Kunlun, Altay and Tianshan is them a instep of the Project of Snow Leopard in X injiang supported by the International Snow Leopard Trust ( SLT) and the Xinjiang Conservation Fund (XCF). During the field survey from 2004 to 2010, the Xinjiang Snow Leopard Group ( XSLG) spent about 270 days in over 20 different places, covering over 150 transects totaling nearly 190 km, and found 1- 3 traces per kilometer. The traces of snow leopard recorded include dung, odor, chains of footprints, scraping, paw nail marks, lying mark, fur, urine, bloodstain, leftover of prey corpse, roaring and others. Based on tracer image analyses, the XSLG got to know primarily scopes of the domains, distribution and relative density of the snow leopard in these areas. Then the group began to take infrared photos, conducted survey of food sources of the leopards, investigated fur market and paths of trading, and cases of killing, and carry out civil survey through questionnaire, non government organization community service and research on conflicts between grazing and wild life protection. A total of 36 infrared came ras were laid out, working a total of about 2 094 days or 50 256 hours. A total 71 rolls of film were collected and developed, includ ing 32 clear pictures of snow leopards, thus making up a shooting rate or capture rate of 1.53%. It was ascertained that in Tomur Peak area, there were 5- 8 snow leopards roaming within a range of 250 km2, forming a population density of 2��0- 3��2 per 100 km2. After compar ing the various monitoring results, the advantages and limitations of different monitoring methods have been discussed.
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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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