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    Ecology and Management of swamp deer (Cervus duvauceli duvauceli) in Dudhwa Tiger Reserve, U.P. India
    (Wildlife Institute of India, Dehradun, 1995) Qureshi, Q.; Sawarkar, V.B.; Mathur, P.K.
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    Wildlife Conservation, Research and Management
    (Wildlife Institute of India, Dehradun, 2005) Jhala. Y.V.; Chellam, Ravi; Qureshi, Q.
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    Developing a Trans-boundary Conservation Landscape for the Eastern Himalaya: an ecological assessment of alpine habitats in Khangchendzonga Biosphere Reserve, Sikkim
    (Wildlife Institute of India, Dehradun, 2006) Rawat, G.S.; Tambe, Sandeep
    Alpine areas of Khangchendzonga Biosphere Reserve (KBR), Sikkim were surveyed during summer-monsoon of 2006 with the following objectives: (i) Conduct a rapid survey of alpine vegetation communities / physiognomic units vis-a-vis alpine habitats, (ii) Characterize and classify the alpine habitats for major faunal groups and assess the anthropogenic pressures and grazing by the domestic livestock, (iii) Identify key floral assemblages / threatened plants of high conservation significance^ and (iv) Suggest a zonation plan and measures for long term conservation and monitoring of alpine habitats and review the trans-boundary issues. The alpine zone in KBR is spread over Greater and trans-Himalaya and covers nearly 48 % of the reserve. This area harbours a large number of rare and threatened mammals such as Himalayan musk deer (Mochus chrysogaster), Himalayan tahr (Hemitragus jemlahicus), blue sheep (Pseudois nayaur), snow leopard (Uncia uncia) and a variety of avifauna. The land use practices in the BR and adjoining areas of Nepal include traditional livestock (yaks, cow-yak hybrids, horses and sheep) grazing, collection of medicinal and aromatic plants and tourism. The area is contiguous with the Kanchenjunga Conservation Area of Nepal. Both the areas, altogether^ promise an excellent potential for a transboundary peace park. Broad vegetation types and alpine habitats have been classified and described in detaiL Based on broad physiognomy and land forms following broad habitat types have been identified in the alpine zone of KBR: Krummholtz Zone, Alpine Scrub, Alpine Meadows, High Altitude Lakes, Moranic Environs, Inaccessible rocky and cliff areas, Riverine Habitats, and Special Habitats (caves, tallus, colluvial deposits). Dominant vegetation types, human use and wildlife within each habitat have been given. Based on the earlier literature and extensive floral survey a tentative list of vascular plants in alpine areas of KBR has been prepared (Appendix - 2) giving their habit, altitudinal zone and threat status. Several plant species of high conservation value have been identified e.g.9 Schizandra grandiflora (a primitive climber with flowers like miniature Magnolia). Helwiga hinmlaica (bearing flowers at the center of the leaf and endemic to the Eastern Himalaya) Circaeaster aqrestis (Chloranthaceae of uncertain affinity), Pinguicula alpina (an insectivorous plant), Triosteum himalayanum (endemic to Himalaya) and Brachycaulos simplicifolius (an unusual herb of Rosaceae) among others. Various trans-boundary issues in the KBR including trans-boundary cultural ties, trade in medicinal plants, pastoralism, historical barter system, etc have been identified and discussed. Based on the detailed analysis of the issues and field surveys of selected areas along with the frontline staff of KBR various management recommendations have been given which include more multidisciplinary surveys in the KBR, training programmes for the frontline staff of KBR and Himal Rakshaks, notification of botanical hotspots within KBR for future monitoring, and better management of trail and camping sites in KBR. The authorities of Kanchenjunga Conservation Area in Nepal, and PA Managers in India need to begin a dialogue afresh to revive Singalila Transborder Eco-tourism and set up a long term trans-border peace park for joint protection and management involving the local communities.
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    Ecological study of tiger beetles (Cicindelidae) as indicator for biodiversity monitoring in the Shivalik landscape
    (Wildlife Institute of India, Dehradun, 2007) Uniyal, V.P.; Sivakumar, K.; Padmawathe, R.; Kittur, Swati; Bhargav, Vinay; Bhardwaj, Manish; Dobhal, Rashmi
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    The Nicobar megapode Megapodius nicobariensis status, ecology and conservation : aftermath tsunami
    (Wildlife Institute of India, Dehradun, 2007) Sivakumar, K.
    The Wildlife Institute of India conducted a status survey of the Nicobar megapode along with other coastal endangered species in the Nicobar group of islands in an effort to document the adverse impacts on their populations due to tsunami that occurred on 26th December 2004. The endemic Nicobar megapode population showed a dramatic decline (nearly 70%) in the number when compared to previous survey carried out in 1993-94. In 2006, there are approximately 800 breeding pairs in the coastal zo nes of these island group. 2. There was no evidence of Nicobar megapode in Megapode Island WLS and Trax Island during this survey where megapodes was reported earlier. 3. Crucial megapode habitats such as littoral forests of the island group were adversely affected. The populations of indicator species of the littoral forests Barringtonia asiatica and Terminalia bialata were severely impacted. However, regeneration of these species was found on the coastal region. 4. The island ecosystem are known for their resilience due to their ability for repopulating habitats and promoting regeneration. However, the restoration of the original biodiversity is possible only if the natural process such as recolonization is facilitated. The aftermath of the tsunami has left the trail of homeless families who need rehabilitation. Finding proper homes and alternate livelihood for them should not undermine ecosystem resilience. Raising plantation crops to generate revenue in the littoral forests should take into account the long term effects of habitat alteration. 5. Significant levels of wildlife habitats have been occupied by the tribals under the leadership of the tribal chiefs (known as Village Captain). Any conservation awareness programme with the help of these Village Captains would be useful for implementing recovery plans of declining species. 6. The Nicobar Division of the State Forest Department needs to be strengthened to facilitate wildlife protection and to take up appropriate wildlife management actions. 7. A total of 37 permanent monitoring plots have been identified and marked (Table 2) for long term monitoring of megapodes and its habitat. With some basic training, forest staff can collect data from these plots and within a weeks time all islands can be surveyed and collected data analyzed for developing appropriate conservation and management measures.
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    Recovery of dugongs and their habitats in India: an integrated participatory approach : Annual Progress report VI (2021-23)
    (Wildlife Institute of India, Dehradun, 2023) Johnson, J.A.; Prabakaran, N.; Sivakumar, K.; Chakraborty, O.; Gole, S.; Pathan, S.; Ghanekar, C.; Rajpurkar, S.; Hatkar, P.; Seal, S.; Patel, S.; Iyer, S.; Prajapati, S.; Bose, S.; Tripura, V,; Christian, G.; Joshi, R.; Aggarwal, A.; Dhiman, G.; Negi, S.
    National CAMPA Authority under the aegis of Endangered Species Recovery Program, Dugong Recovery Program was initiated with major objectives to a) Assess dugong population status through advanced census techniques and determine its abundance and distribution, identify critical habitats, classify threats and develop a site-specific monitoring plan to reduce poaching and incidental entanglements, b) Characterize the critical dugong habitats, reduce direct and indirect threats, c) Raise awareness on the species and encourage the participation of the local communities; and d) Enhance the capacity of the State Forest Department staff and develop/implement smart patrolling tools to improve protection enforcement; train forest staff and local communities in underwater surveys for long-term habitat monitoring. In the last five years of its implementation, an integrated participatory approach was adopted to ensure recovery of dugong populations and conservation of seagrass habitat in India.
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    Habitat ecology and conservation status of wild ungulates in Northern parts of Changthang Wildlife Sanctuary, Ladakh
    (Wildlife Institute of India, Dehradun, 2011) Rawat, G.S.; Sankar, K.
    An ecological study on the wild ungulates was carried out in the northern parts of Changthang Wildlife Sanctuary, Ladakh during 2007 – 2009 with a view to ascertain the population status, distribution and habitat use pattern. The five species of sympatric ungulates found in this part of Trans-Himalaya include chiru or Tibetan antelope (Pantholops hodgsoni), wild yak (Bos mutus), Tibetan argali (Ovis ammon), kiang (Equus kiang) and blue sheep (Pseudois nayaur). Specific objectives of the study were: (i) To study the population status and distribution of wild ungulates in northern parts of Changthang WLS, (ii) To study the habitat characteristics and habitat use by the ungulates, (iii) To identify the major threats and suggest conservation strategies, and (iv) To evolve protocol for monitoring wildlife populations in the study area. 2.The study area was located in the north and north-east of Pangong Tso covering Phobrang surrounds and Changchenmo Valley which vary in altitude from 4450 to 5800m asl. The entire landscape is spread over an area of >3100 km2. However, intensive study was conducted within <500 km2 around Phobrang and Changchenmo. The study area is characterized by cold arid environment with very sparse vegetation cover which can be categorized into moist and mixed meadows, desert steppe and scrub steppe. About 12% geographical area is covered by perpetual snow and glaciers, 1.6% area is represented by moist and marsh meadows and over 84% area is under sparsely vegetated desert steppe which is further divisible into various landscape units and habitat types. The study area is the only place within Indian territory where these five sympatric ungulates co-exist.3.Based on a reconnaissance trip we classified the study area into various strata. Field work was carried out during 2007 – 2009 covering two summer and one winter season. Line Transects and trail monitoring were followed for the collection of data on population structure, status and distribution of ungulates in various areas on seasonal basis. In each strata transects varying in length of 6-8 kms were walked. A total of 503 km were monitored in 42 trails, spending 249.85 hrs of observation. Data based on direct sightings and indirect evidences of ungulate species were recorded along transects in the survey blocks. Habitat parameters were quantified using standard methods. Conservation and management issues were identified based on primary and secondary data collected from the survey area.4.The study reveals that of the five species of sympatric ungulates, chiru and wild yak use only parts of Changchenmo Valley while remaining three species are found in both the areas. In Changchenmo Valley we estimate a population of 20 – 30 chiru, 110 – 120 wild yak, 125 – 150 kiang, 120 - 130 blue sheep and 35 – 50 Tibetan argali. Based on the past reports and present study we conclude that number of chiru population in Changchenmo Valley is on decline. Our study reveals that chiru males do use Changchenmo Valley during winter. For the first time, we report a new location of chiru i.e., Thratsang La in Changthang plateau.5.Blue sheep, being smallest of all the ungulates, selected steep and glaciated zones with short forbs and a few graminoids. Chiru males and wild yak were confined to eastern part of Changchenmo Valley, especially with higher cover of graminoids (Carex moorcroftii, Stipa purpurea, Leymus secalinus and Scirpus sp.). Kiang occupied most of the habitat categories except steep slopes and cliffs. Highest altitudes were used by blue sheep followed by wild yak, Tibetan argali, chiru and kiang. Kiang and argali showed preference for south facing slopes while other species used in proportion to availability.The major conservation issues in the study area include (i) Small and fragmented populations of threatened ungulates, (ii) Degradation of rangelands and loss of productivity, (iii) Possible genetic contamination of wild yak, (iv) Presence of feral dogs around security camps, (v) Lack of alternate livelihoods for the local people, (vi) Inadequate infra-structure and man power for the PA management. Appropriate recommendations to deal with above issues have been given.The study area is partly controlled by the Indian security personnel, who have taken keen interest in the conservation and monitoring of threatened wildlife in the area. A detailed monitoring protocol based on vehicle survey, on-foot patrol and animal observations from the fixed positions have been suggested.