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Ganhar, J. (1979). The Wildlife of Ladakh. Srinagar, India: Haramukh Publications.
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Chalise, M. K. (2008). Wild Fauna around the Himalayan Wetlands. In W. O. S. & Sung-Hoon S. Bhandari B.B. (Ed.), Water Tower of Asia: Experiences in Wetland Conservation in Nepal (pp. 104–108). South Korea.
Abstract: The Himalayan mountain range extends in a broad arc from Pakistan through India, Nepal, Bhutan and China. With elevations ranging from approximately 300 meters in the plains at the base of the mountains to the peaks well over 8,000 meters (Mt Everest 8,848 m). The Himalaya is the tallest and most complex of the world mountain regions (Striffler, 1985). The Himalaya can be divided into three physiographic zones. These includes the lower foothills usually describe as sub-Himalaya and represented by the Siwalik Hills which extend along most of the Himalaya with elevation seldom exceeding 1000 m. The second zone is the middle Himalaya also called Outer Himalaya or the lesser Himalaya with elevation ranges from 600 meters to over 3000 m. Interspersed within the middle zone are occasional larger to small valleys and river basins. The third zone is the great Himalaya or Inner Himalaya zone that covers higher mountain areas, the snow clad peaks and trans-Himalayan harsh climatic dry areas (HMG Nepal, 1977; Kaith, 1960). The glaciers and natural springs have drained the whole area and created a vast area as wetlands supplemented by different lake system in different elevations.
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Khatiwada, J. R. & C., M.K. (2007). Important fauna of Himalaya around Wetland. In Bhandari B.B. & Gea J.J. (Ed.), Himalayan Wetlands: Risk, Challenges and Opportunities (pp. 52–58). South Korea.
Abstract: Wetlands are classified according to landscape where they are found. For
example they are high altitude wetlands, mountain wetlands. When said high
altitude wetlands, they are lakes, ponds, rivers, glaciers, glacial lakes,
meadows, etc. in high altitude areas. Bhandari (2005) has defined "High
Altitude Wetlands are those types of wetlands which are found above the
elevation of 3,000 masl". They are generally above the tree line.
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Jackson, R., Roe, J., Wangchuk, R., & Hunter, D. (2005). Surveying Snow Leopard Populations with Emphasis on Camera Trapping: A Handbook. Sonoma, California: The Snow Leopard Conservancy.
Abstract: This handbook provides an introduction to snow leopard population survey techniques, followed by a detailed account of camera trapping methods.During the 2002 through 2004 winter field seasons, the Snow Leopard Conservancy experimented with infrared camera trapping techniques to define a methodology suitable for the high altitude environment.
In 2001 and 2002, much of our time was spent familiarizing ourselves with various infrared camera traps, their operation and setup, and comparing the effectiveness of different models and sensor types. We placed infrared camera traps along frequently used travel corridors at or near scent-sprayed rocks (rock scents) and scrape sites within 16 km2 sampling cells between January and March in 2003 and 2004. A total of 66 and 49 captures of snow leopards were tallied during 2003 and 2004, resulting in an overall capture success of 8.91 and 5.63 individuals per 100 trap-nights, respectively. Capture probabilities ranged from 0.33 to 0.46. Density estimates ranged from 8.49 ± 0.22 individuals per 100 km2 in 2003 to 4.45 ± 0.16 in 2004, with the disparity between years largely attributed to different trapping densities. Snow leopard abundance estimates were calculated using the computer program CAPTURE.
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Jackson, R., Roe, J., Wangchuk, R., & Hunter, D. (2005). Surveying Snow Leopard Populations with Emphasis on Camera Trapping: A Handbook. Sonoma, California: The Snow Leopard Conservancy.
Abstract: This handbook provides an introduction to snow leopard population survey techniques, followed by a detailed account of camera trapping methods.During the 2002 through 2004 winter field seasons, the Snow Leopard Conservancy experimented with infrared camera trapping techniques to define a methodology suitable for the high altitude environment.
In 2001 and 2002, much of our time was spent familiarizing ourselves with various infrared camera traps, their operation and setup, and comparing the effectiveness of different models and sensor types. We placed infrared camera traps along frequently used travel corridors at or near scent-sprayed rocks (rock scents) and scrape sites within 16 km2 sampling cells between January and March in 2003 and 2004. A total of 66 and 49 captures of snow leopards were tallied during 2003 and 2004, resulting in an overall capture success of 8.91 and 5.63 individuals per 100 trap-nights, respectively. Capture probabilities ranged from 0.33 to 0.46. Density estimates ranged from 8.49 ± 0.22 individuals per 100 km2 in 2003 to 4.45 ± 0.16 in 2004, with the disparity between years largely attributed to different trapping densities. Snow leopard abundance estimates were calculated using the computer program CAPTURE.
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The Snow Leopard Conservancy. (2003). Local People's Attitudes toward Wildlife Conservation in the Hemis National Park, with Special Reference to the Conservation of Large Predators (Vol. 7). Sonoma, California.
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Xu, H. F., Zhang, E. D., & Song, H. G. (1998). Wildlife conservation and management principles and techniques. Shanghai: East China Normal University Press.
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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.
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International Snow Leopard Trust. (2002). Snow Leopard News, Spring 2002. Seattle, Washington: Islt.
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Woodland Park Zoological Gardens. (1982). Symposium held on snow leopard. Woodland Park Zoological Gardens Newsletter, , 1–3.
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