India contains c. 2% of the global snow leopard Panthera uncia range, with 400–700 individuals distributed along the sub-alpine, alpine and trans-Himalayan regions of Ladakh, Jammu and Kashmir, Himachal Pradesh, Uttarakhand, Sikkim and Arunachal Pradesh (McCarthy et al., Reference McCarthy, Mallon, Jackson, Zahler and McCarthy2017; Sharma & Singh, Reference Sharma and Singh2020). The snow leopard is an iconic species and an ideal flagship for the conservation of these high-altitude mountain ecosystems (McCarthy et al., Reference McCarthy, Mallon, Jackson, Zahler and McCarthy2017). The occupancy and abundance of the snow leopard is poorly known across its range in India (Suryawanshi et al., Reference Suryawanshi, Khanyari, Sharma, Lkhagvajav and Mishra2019; Sharma & Singh, Reference Sharma and Singh2020). Population surveys in the Western Himalayas have been limited to Ladakh, Himachal Pradesh and Uttarakhand (Ghoshal et al., Reference Ghoshal, Bhatnagar, Pandav, Sharma, Mishra, Raghunath and Suryawanshi2019). In Kashmir the snow leopard has been reported from Gurez and Sonamarg (Ahmad et al., Reference Ahmad, Sultan, Naqash and Baba2020), in the upper Baltal-Zojila region (Hussain, Reference Hussain2022), in the Kargil range (Maheshwari et al., Reference Maheshwari, Takpa, Angchok, Rauf and Ali2012) and in the areas adjacent to the north-eastern and south-eastern boundary of Kishtwar that connect with the Zanskar range in the Union Territory of Ladakh (Snow Leopard Conservancy, 2018; Fig 1). However, its occurrence remains uncertain in the majority of Kashmir, including in protected areas. Here we report the first photographic records of snow leopards in Kishtwar High Altitude National Park, through camera trapping. Prior to this there were reports of snow leopard presence in the area based on signs (Hilaluddin & Naqash, Reference Hilaluddin and Naqash2013) and a sighting record (Zaheer et al., Reference Zaheer, Sofi, Sarkar, Amin and Bashir2023), although neither of these reports included photographic evidence.
The 2,191 km2 Kishtwar High Altitude National Park covers an altitude range of 1,800–6,000 m above the Chenab River and below the Nagin Sheer glacier, connected with Ladakh through the Zanskar range to the north-east and Himachal Pradesh to the south (Fig. 1). The Park is largely inaccessible above 4,300 m because of the rugged terrain and extreme weather. The Park has several vegetation types across its wide variation in elevation, aspect, slope and moisture regime (Sharma et al., Reference Sharma, Rana, Raina, Amir and Kichloo2018). The Semi-Arid Biogeographic Zone, which defines the north-eastern border of the study area, is a mosaic of biomes. This encourages the inward movement of several species of mammals, including the wolf Canis lupus, Siberian ibex Capra sibirica, Himalayan musk deer Moschus leucogaster and snow leopard. The National Park supports the livelihoods of thousands of nomadic livestock herders and also attracts pilgrims to several temples in the Kibber and Nanth catchments.
Using ArcGIS 9.3 (Esri, USA), we divided the study area into a grid of 5 × 5 km cells and deployed 40 camera traps (Cuddeback Blue Series 1279 and 1248, Cuddeback, USA) at 57 locations in a total of 18 grid cells for 1 year (May 2022–June 2023). We deployed cameras on natural trails, trail junctions, ridge lines and locations of probable animal use, based on the occurrence of carnivore signs, to maximize the probability of detecting animals. We deployed 1–4 cameras in each grid cell, for a minimum duration of 1 month at each location, after which we moved cameras to new locations to ensure maximum coverage. We checked the cameras at least once per month (except during winter) to ensure they were functioning and to replace batteries and memory cards. As a large part of the National Park is glacier covered (including northern, north-eastern, eastern and south-eastern regions above 4,500 m) and thus mostly inaccessible, the positioning of our camera traps was limited to the southern, south-western and central areas of the Park. However, we are continuing our camera-trap surveys in the Park, with wider coverage.
During 6,623 trap-nights we obtained photographs of two individual snow leopards in a single frame on 19 September 2022 at 23.03 in the Kiyar catchment of the Dacchan range at 3,280 m. This was the first photographic evidence of the species in Kishtwar High Altitude National Park (Plate 1a). We obtained seven more photographs of snow leopards in three other grid cells, in the Kiyar and Nanth catchments of the Dacchan range and the Renai catchment of the Marwah range (Fig. 1). Of the eight captures, we recorded four during the day and four during the night, with an overall capture rate of 0.123 ± SE 0.072 captures/100 trap-nights. Based on their coat patterns, we identified at least four different individuals. The eight captures were at 3,004–3,878 m altitude. This is mostly an arid alpine region above the treeline, with steep and rugged terrain flanked by high-altitude pastures of junipers Juniperus spp., grasses and legumes on rolling hills.
During reconnaissance surveys, trail monitoring and camera trapping we also recorded the presence of ungulates such as the Siberian ibex and Himalayan musk deer, which have been reported previously in this area (Kichloo et al., Reference Kichloo, Sohil and Sharma2023), and small mammals, including the long-tailed marmot Marmota caudata and pika Ochotona sp. These species are considered potential snow leopard prey (Lyngdoh et al., Reference Lyngdoh, Shrotriya, Goyal, Clements, Hayward and Habib2014). Of these, the highest camera-trap capture rate was of the Siberian ibex (Table 1). We also recorded other carnivore species with the camera traps (Himalayan brown bear Ursus arctos, Asian black bear Ursus thibetanus, red fox Vulpes vulpes, leopard cat Prionailurus bengalensis, yellow-throated marten Martes flavigula and mountain weasel Mustela altaica), amongst which we recorded the highest photo capture rate for the red fox. The generally greater detection of carnivores compared to prey could be attributed to our survey design, which focused on trails, trail junctions and ridge lines used by carnivores.
We also documented significant anthropogenic pressure through livestock grazing at higher elevations in the Kibber, Kiyar, Nanth and Renai catchments. Nearly 3,000 graziers and nomadic herders visit the alpine pastures in the Marwah range each year, with c. 150,000 livestock (Hilaluddin & Naqash, Reference Hilaluddin and Naqash2006). Overstocking is therefore a threat to both the habitat and the wild ungulate prey of the snow leopard through competition for pasture. This could lead to human–wildlife conflict and drive the snow leopard and its prey into suboptimal areas, thus exposing them to other threats. Our camera-trapping results indicate an avoidance of livestock-grazing areas by snow leopards and wild ungulates during summer (May–August), with no detections of these species during these months. This could have significant conservation implications and requires further examination.
Our findings indicate that Kishtwar High Altitude National Park is potential snow leopard habitat. This region connects three Himalayan landscapes: the greater Himalayas of Jammu and Kashmir, the trans-Himalayas of Ladakh (through Zanskar) and the lesser Himalayas of Himachal Pradesh (Baba, Reference Baba2003; Kichloo & Sharma, Reference Kichloo and Sharma2021). Given the geographical position of the Kishtwar landscape and its high-altitude passes that connect snow leopard populations in the Himalayan and trans-Himalayan regions (Snow Leopard Conservancy, 2018; Kothari, Reference Kothari2022) to the global snow leopard range (Fig 2), our findings are important for snow leopard conservation in India. We recommend that a comprehensive study is conducted over the entire Kishtwar landscape (including the Paddar and Wadwan valleys) to estimate the occupancy and abundance, and demography and movement patterns of snow leopards and their prey. In addition, evaluation of their interactions with pastoral communities and threats to the conservation and management of this important high-altitude region is needed.
Acknowledgements
We thank the Department of Wildlife Protection, Jammu and Kashmir, for providing research permits M.K. Kumar, IFS, Regional Wildlife Warden Jammu, for supporting us throughout the study; the Wildlife Biology Laboratory at the Centre of Research for Development, University of Kashmir, and the National Development Foundation, Jammu for the academic and logistical support. We also thank the field assistants from Kishtwar village for their help with the data collection. This study was funded by the Department of Wildlife Protection, Jammu and Kashmir, through a research project sanctioned to the National Development Foundation, Jammu.
Author contributions
Conceptualization: TB, PC; data collection, field surveys: OS, MR; data analysis: OS; research design and interpretation: TB; writing: OS, TB; resources and supervision: TB, PC; research permission: PC; revision: OS, TB, PC.
Conflicts of interest
None.
Ethical standards
Our study is based on field data collected through non-invasive sampling. We conducted our camera-trap placement in a socially responsible manner that did not violate privacy or cause other unnecessary harm. Our research received the necessary approvals and permits from appropriate institutions and statutory authorities of Jammu and Kashmir. No ethical approval was required for this research, and it otherwise abides by the Oryx guidelines on ethical standards.
Data availability
The data supporting our findings are available on request from the corresponding author.