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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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Fox, J. (1989). Snow Leopard. Panthera uncia Schreber 1776.
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Jackson, R. (1992). SCC Plan for snow leopard.
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International Snow Leopard Trust. (1998). ISLT Hires Snow Leopard Conservationist in India.
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Mazoomdaar, J. (2011). Cat Among the People. Open, (8 August), 40–45.
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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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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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The Current Digest of the Soviet Press. (1979). Soviet Zoos: Limited in Imagination, Space and Numbers. The Current Digest of the Soviet Press, XXXL(23), 5.
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Dickman, A., Macdonald, E., Macdonald, D. (2011). A review of financial instruments to pay for predator conservation and encourage human–carnivore coexistence. PNAS, 108(34), 13937–13944.
Abstract: One of the greatest challenges in biodiversity conservation today is how to facilitate protection of species that are highly valued at a global scale but have little or even negative value at a local scale. Imperiled species such as large predators can impose significant economic costs at a local level, often in poverty-stricken rural areas where households are least able to tolerate such costs, and impede efforts of local people, especially traditional pastoralists, to escape from poverty. Furthermore, the costs and benefits involved in predator conservation often include diverse dimensions, which are hard to quantify and nearly impossible to reconcile with one another. The best chance of effective conservation relies upon translating the global value of carnivores into tangible local benefits large enough to drive conservation “on the ground.” Although human–carnivore coexistence involves significant noneconomic values, providing financial incentives to those affected negatively by carnivore presence is a common strategy for encouraging such coexistence, and this can also have important benefits in terms of reducing poverty. Here, we provide a critical overview of such financial instruments, which we term “payments to encourage coexistence”; assess the pitfalls and potentials of these methods, particularly compensation and insurance, revenuesharing, and conservation payments; and discuss how existing strategies of payment to encourage coexistence could be combined to facilitate carnivore conservation and alleviate local poverty.
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WWF Russia & Mongolia. (2011). WWF Newsletter Altai-Sayan Ecoregion July – September 2011.
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