WII Technical Reports
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Item Impact of artificial illumination on sea finding behaviour of olive ridley sea turtle at Gahirmatha Rookery, Odisha. Report submitted to the Directorate of lighthouses and lightships(Wildlife Institute of India, Dehradun, 2025) Pandav, Bivash; Kumar, R.S.This study has the following objectives: I. To study the impact of artificial illumination on nesting sea turtles using the Gahirmatha rookery. II. To assess the level of disorientation by turtle hatchlings and suggest measures to minimize this.Item Management Effectiveness Evaluation of National Parks and Wildlife Sanctuaries in India(Wildlife Institute of India, Dehradun, 2020) Mohan, D.; Talukdar, Gautam; Sen, M.; Ansari, N.A.Item Assessment of impacts of State highway 33 on flora and fauna of Nagarhole Tiger Reserve, India(Wildlife Institute of India, Dehradun, 2020) Habib, BilalAs part of the project funded by the National Tiger Conservation Authority, New Delhi, three sites were chosen for study- the Central Indian tiger landscape including major roads cutting across the animal corridors in the landscape, the National Highway 37 (now 715) cutting through the Kaziranga-Karbi Anglong landscape in Assam, and the State Highway 33 passing through the Nagarhole Tiger Reserve, Karnataka. At Nagarhole Tiger reserve, we intended to study the difference in the impacts of the SH 33 along its two stretches – one that is completely closed to traffic (decommissioned segment) and the other stretch that is closed for night time traffic (night traffic closed segment). We compared the floral (tree species composition and richness), and faunal (ungulate group size and composition, habitat use and activity patterns) characteristics along the two road stretches. We found that tree and sapling species richness was found to be higher in the decommissioned road segment as compared to the night traffic closed road segment, both of which comprised predominantly of native vegetation. On the other hand, shrubs and herbs had higher species richness in the night traffic closed road segment. We found higher species richness and cover of grasses, shrubs and herbs in the night traffic closed road segment, which can be attributed to the edge effect. Even though both the segments of the highway under study are homogenous in respect of rainfall regime, forest type and are managed as part of national park under the same management objectives (Gubbi et al. 2012), results of shrub and sapling study indicate that there exists some distinguishing factors along the two segments so as to favor different species. A further detailed study is required to point out the factors responsible. Contrary to the general understanding, invasive species cover for two of the common invasive species (Lantana camara and Eupatorium odoratum) was higher in the area devoid of traffic as compared to the night traffic closed road segment. This can be attributed to increased light intensity on the forest floor due to lower canopy cover in the decommissioned road segment and higher animal activity, who acts as seed dispersers. Lower canopy cover in decommissioned road segment can be the result of breakage of canopy and crushing of new regeneration by higher presence and more frequent activity of large mammals, like elephants. Mean group size of chital was found to be higher in the night traffic closed road segment, whereas mean crowding was higher in the decommissioned road segment. Higher presence of chital in the night traffic closed road segment can be because of availability of more fodder species and less risk of predation. In the decommissioned road segment, chital and wild pig’s habitat use is not affected by the distance from the state highway, whereas, sambar and elephant’s habitat choice is determined by distance from the highway. There has been a 16% increase in the traffic volume from 553 vehicles /day in the last 9 years as reported by Gubbi et al. (2012), to 659 ± 139.70 as reported in our study. However, though there has been an increase in the traffic volume, it is at a slower rate as compared to the increase from 2003 to 2010 level. The average speed of vehicles ranged from 27.5 MPH to 35.4 MPH. We found that in the night traffic closed road segment, animals have modified their activity periods to avoid the vehicular traffic. Most of the mammals are either active in the early morning hours before the road is opened for vehicular movement or late evenings after the road is closed. This suggests that there is a difference in activity pattern of these mammals along both the road segments, in order to understand which a further detailed study about behavior modification of mammals in relation to traffic and other road related disturbances needs to be carried out.Item Preliminary assessment of tigers, co-predators and prey in Pranhita Wildlife Sanctuary, Maharashtra, India for exploring options for conservation translocation(Wildlife Institute of India, Dehradun, 2020) Habib, B.; Nigam, P.; Joshi, K.; Panwar, P.As part of the project “Preliminary assessment of tigers, co-predators and prey species in Pranhita Wildlife Sanctuary, Maharashtra, India for exploring options for conservation translocation”, the study was carried out in Pranhita Wildlife Sanctuary in Gadchiroli district of Maharashtra. The fieldwork was carried from January 2019 to June 2019 covering an area of 418.85 km2 in southern Gadchiroli. The Eastern Vidarbha Landscape (EVL) holds a high density of carnivores both inside and outside protected areas leading to an increase in human-wildlife interactions. Pranhita Wildlife Sanctuary (PWLS) is a part of EVL and could be an important corridor. To explore new habitats for carnivore species, we conducted a preliminary assessment of tigers, co-predators, and prey in PWLS. The sanctuary mainly is dominated by Southern Tropical Dry Deciduous forest. We conducted carnivore and ungulate sign surveys and deployed camera traps (n=25) in 40 km2 area in Bahmni range. The area was divided into different 1.42 × 1.42 km2 grids and at least one pair of camera trap was placed in each 2.0164 km2 grid at 20 sites and operated for 24-27 days in Bahmni range. Apart from that random camera traps were placed at 5 sites in Kamlapur and Pranhita ranges for 1 to 7 days during the study period. The camera traps sampling effort was 1030 trap nights and around 33000 images were captured. For prey species density estimation, 24 line transects of 2 km length were walked in 43 beats with 5-7 replicates. For vegetation quantification, we laid a total of 144 circular plots of a 10-meter radius and recorded 43 trees, 37 shrubs, and 13 grass species. We used both spatial and temporal data for occupancy estimation. Data were analyzed using the software Presence for occupancy estimation and Distance 7.2 for density estimation. A total of 10 carnivore species were recorded directly or indirectly during the study period. According to the IUCN Red List of threatened species, 2 are Endangered and Near Threatened, and 2 are vulnerable. The major carnivore species are leopard, Asiatic wild dog, sloth bear, Indian grey wolf, jungle cat, Indian fox, and rusty-spotted cat. The occupancy estimate (ψ) of leopard in the null model was 0.20 while for other carnivore species like sloth bear, jungle cat and wild dog were 0.70, 0.74, and 0.68 percent respectively. A total of 14 prey species were recorded during the line transect and sign survey. The major prey species are sambar, Indian gaur, chousingha, Indian giant squirrel, chital, wild pig, nilgai, barking deer, langur sp., rhesus macaque, and Indian peafowl. Among these, 3 species are listed as Vulnerable and 1 as Near Threatened by IUCN Red List. Overall density estimation of major ungulate species was 14.82/km2. The encounter rate of cattle was 0.17/km, nilgai 0.039/km, chital 0.059/km, chousingha 0.016/km, and wild pig 0.022/km. Individual density estimate of major ungulate species like chital 2.27/km2, wild pig 11.55/km2, nilgai 0.72/km2, langur 0.55/km2, Indian hare 1.78/km2, peafowl 0.44/km2, grey jungle fowl 1.87/km2, chousingha 0.28/km2 and cattle were 28.61/km2. Occupancy estimate of ungulate species like sambar 0.27%, chital 0.44%, chousingha 0.51%, Indian gaur 0.07% and nilgai were 0.59%. The major threats in the sanctuary areas are hunting for local consumption, tree cutting, livestock grazing, forest fire, roadkill, and electrocution. We have got 28 % usable images of cattle grazing and 4 % of hunting. Other administrative lacunas are impractical beat boundaries, unequipped frontline staff, lack of legal action against the guilty, inadequate infrastructure, lack of training and capacity building. There is a consistent trepidation of left-wing extremism in the minds of locals and forest officials. It prevents or demotivates them from working efficiently in the PWLS. These activities directly or indirectly affect wildlife conservation and management in PWLS. This was the first-ever scientific study conducted to document prey and predator presence in PWLS. Further detailed and long-term studies are required for a better understanding of species ecology and their habitat. Such studies will help not only in better management and conservation of species in the area but also in decision-making on conservation translocations. Based on the preliminary study and SWOT analysis following are measures to be taken before translocation of any large carnivore species to Pranhita Wildlife Sanctuary: 1. Capacity building of local staff for effective wildlife management.2. Enhancement of protection measures in the Sanctuary to reduce poaching, hunting, and other illegal activities. 3. Habitat improvement by grassland management and eradication of lantana and other invasive species. 4. Reducing threats due to electrocution by illegal power fences used for local hunting and protection of crop fields by local farmers. 5. Special forest protection force for Gadchiroli considering extremism issues.6. Augmentation of the prey base to enhance fast recovery of prey species.7. Maintaining full-strength dedicated forest staff across all range offices of the division.8. Building infrastructure such as patrolling roads, forest chowkis etc., across the sanctuary.9. Involving local people in conservation measures across the sanctuary.10. Establishment of local ecodevelopment committees. 11. Wildlife-oriented management across the Gadchiroli forest division.12. The special financial package for Gadchiroli for enhancing wildlife-oriented management.13. Mitigation measures on the existing roads through the sanctuary and other critical wildlife corridors across the division.14. Implementation of Shyamaprasad Mukherjee Jan Van Vikas Scheme for development of villages across the forested landscape of Gadchiroli to achieve sustainable development of these villages and reduce the man-animal conflict.15. Identification of potential areas within the district for designation as Sanctuary, National Park, Conservation Reserve, Community Reserve.Item Assessment of impacts of National Highway 715 (Earlier NH 37) on Wildlife passing through Kaziranga Tiger Reserve, Assam(Wildlife Institute of India, Dehradun, 2020) Habib, Bilal; Saxena, Akansha; Bhanupriya, R.; Jhala, Y.V.; Rajvanshi, A.As part of the project funded by the National Tiger Conservation Authority, New Delhi, three sites were chosen for study- the Central Indian tiger landscape including major roads cutting across the animal corridors in the landscape, the National Highway 37 (now 715) cutting through the Kaziranga-Karbi Anglong landscape in Assam, and the State Highway 33 passing through the Nagarhole Tiger Reserve, Karnataka. At Kaziranga National Park, we intended to quantify the characteristics of mortality of animals due to wildlife-vehicle collisions, and to assess the responses of wild ungulates to road-related disturbances in terms of changes in group size and composition, and habitat use patterns. Result shows that highways have adverse effects on the population of wildlife including endangered species of mammals and reptiles. Seasonal or monthly changes are the factors that influenced probability of roadkill numbers as it increased with the onset of summer and decreased towards winter. Annual monsoon floods in Kaziranga National Park from adjacent Brahmaputra River was found to be the main factor influencing large mammal mortality in wildlife-vehicle collisions. Apart from the direct impacts of roads on wildlife the indirect impacts like noise and disturbances associated with them impact significantly on the species that require an undisturbed or interior habitat. Similarly, present study exhibits variation in the group size composition of ungulates relative to distance from road. Group-size increased with respect to distance which indicates that anthropogenic effects of roads can lead to the habitat fragmentation of such species affecting population distribution. However, numbers and factors of wildlife-vehicle collisions may vary with site and conditionItem A rapid herpetofaunal assessment in Lower Subansiri and Papum-Pare district, Arunchal Pradesh, India survey report 2020(Wildlife Institute of India, Dehradun, 2020) Das, Abhijit; Boruah, BitupanPresent study yielded 36 species of herpetofauna, of which amphibians represented by 19 species and reptiles by 17 species. All recorded amphibian species are anuran of which, Amolops marmoratus, A. monticola, Raorchestes sp., Zhangixalus smaragdinus, Theloderma asperum, Ingerana borealis and Fejervarya sp. were commonly observed in Potin. In Lichi species such as Euphlyctis cyanophlyctis, Duttaphrynus melanostictus, Fejervarya sp. were commonly encountered. Species belonging to the genus Liurana were only recorded from Talle WLS. Among the recorded reptiles, snake represented by 11 species and lizards represented by six species. Psammodynastes pulverulentus, Cyrtodactylus sp., Sphenomorphus sp. and Calotes jerdonii were frequently recorded in Potin. Study also recorded rare species of reptiles such as Boiga quincunciata and Pseudocalotes austeniana from Potin and Talle WLS respectively. During the study period, species richness was high in Potin as maximum survey was carried out in Potin than that of Lichi and Talle WLS. Few species recorded in the present study are identified upto generic level or referred to closely related species as systematic study of those species is needed. However, the number of herpetofaunal species in the study region will increase with further study as the present study was carried out for a short period. Besides recorded species of herpetofauna, the present study also documents species that were either conferred to closely related species (e.g., Polypedates cf. himalayanus, Asymblepharus cf. sikimmensis) or their identity remains to be ascertained (e.g., Nanorana sp., Raorchestes sp., Cyrtodactylus sp.). However, the present study was carried out for a short period and it indicates the number of herpetofaunal species in the study region will increase with further systematic study. The recordItem Status of Golden Mahseer in River Kosi, Uttarakhand - status report(Wildlife Institute of India, Dehradun, 2020) Johnson, J.A.; Dhawan, Bhawana; Bargali, H.S.; Neha, V.; Sivakumar, K.Item Monitoring of animal underpasses on National Highway 44 (Earlier 7) passing through Pench Tiger Reserve, Maharashtra, India(Wildlife Institute of India, Dehradun, 2020) Habib, Bilal; Saxena, Akansha; Jhala, Y.V.; Rajvanshi, A.As part of the project funded by the National Tiger Conservation Authority, New Delhi, three sites were chosen for study- the Central Indian tiger landscape including major roads cutting across the animal corridors in the landscape, the National Highway 37 (now 715) cutting through the Kaziranga-Karbi Anglong landscape in Assam, and the State Highway 33 passing through the Nagarhole Tiger Reserve, Karnataka. As part of the project, we also monitored the animal underpasses constructed on the National Highway 44 passing through the Pench Tiger reserve, Maharashtra. We used camera traps to capture movement of animals under the nine crossing structures during March-December 2019. We found 18 species of wild animals that were using the crossing structures, with varying frequencies. Seven species of small mammals were found to use the structures. These included Indian hare and jungle cat, which are the most frequent users of the underpasses, and the rare rusty spotted cat. Among wild ungulates, the five major species viz., spotted deer, gaur, nilgai, sambar and wild pig were found to use the structures. Spotted deer and wild pig were the most frequent visitors to the underpasses. Tiger, leopard, wild dog, sloth bear and jackal, the major carnivore species in the landscape, were found using the structures with varying frequencies. Wild dogs were found to use the structures the most, followed by tigers. A total of 89 tiger crossings were recorded from six of the nine structures, by 11 individual tigers.Item Current population status, distribution and threats to Indian pangolin (Manis crassicaudata) in Terai Arc Landscape, Uttarakhand: a pilot study(Wildlife Institute of India, Dehradun, 2020) Lyngdoh, SalvadorThis pilot study to provide information on the current distribution of Indian pangolin and major poaching hotspots throughout its ranges to suggest appropriate conservation strategies and protection measures for the species. The proposed objectives for this pilot study are the following: a. To review the current status, distribution and threats to the Indian pangolin population in the study area. b. To prepare a standard protocol for the survey and population estimation of Indian pangolin. c. To formulate effective anti-poaching strategies and devise conservation measures for Indian pangolin to help Uttarakhand Forest DepartmentItem Habitat improvement and conservation breeding of the Great Indian Bustard and integrated approach. Progress Report April 2019-March 2020(Wildlife Institute of India, Dehradun, 2020) Jhala, Y.V.; Dutta, S.; Karkarya, T.; Awasthi, A.; Bipin, C.M. and othersThe Great Indian Bustard (Ardeotis nigriceps) is critically endangered with 100-150 individuals left, largely in Jaisalmer (Rajasthan) and very small populations in Kutch (Gujarat), Sholapur (Maharashtra), Ballari (Karnataka) and Kurnool (Andhra Pradesh). The species has suffered 90% reductions in number and range, over the last five decades, due to prevalent habitat loss and human induced mortalities compounded with its slow life history traits. The Ministry of Environment, Forest & Climate Change (MoEF&CC) formulated the National Bustard Recovery Plans in 2013 based on scientific consultation, and initiated the Project “Habitat Improvement and Conservation Breeding of Great Indian Bustard” in 2016 with the Wildlife Institute of India (WII) as the nodal agency along with State Forest Departments and partner NGOs as collaborators. This project aims at recovering the species from extinction through holistic approach of conservation breeding, applied research, outreach and pilot habitat management. This report presents the project activities undertaken between 2018-19. 1. The Tripartite Memorandum of Agreement (MoA) for the Great Indian Bustard (GIB) and Lesser Florican conservation breeding and research program was signed between MoEF&CC, Rajasthan Government and WII to operationalize conservation breeding of the GIB under the guidance of a Steering Committee, with facilitation of Rajasthan Government and funding of MoEF&CC. Based on the preliminary surveys carried out by the Project team, two sites – Sorsan, Baran District and Ramdevra, Jaisalmer District were finalized for establishing the Conservation Breeding Center in consultation with the concerned agencies and construction is under progress in Ramdevra. The project team was trained in husbandry practices and veterinary care at the International Fund for Houbara Conservation (IFHC), Abu Dhabi. To utilize the GIB breeding season in 2019-20, as a fully functional pilot project the first GIB Conservation Breeding Center has been established at Sam, Jaisalmer that currently houses ten hand-reared GIB chicks from wild collected and artificially hatched eggs in close collaboration with Rajasthan Forest Department and technical support of International Fund for Houbara Conservation / Reneco. 2. Under the applied research component, three GIB females were radio tagged in Desert National Park, Jaisalmer for understanding bird movements, identifying critical habitats for conservation planning, prioritizing power lines for mitigation, and searching nesting sites for conservation breeding program. Birds have been transmitting data for months from Jaisalmer and Kachchh and providing hitherto unknown basic information on GIB space use and ranging patterns. The average travel distances were similar between the two tagged birds in Thar and almost double than that of Kachchh. Bird home ranges ranged between 76 km2 in Kachchh to 124 km2 in Jaisalmer. The core usages for birds ranged between 13–29 km2 in Jaisalmer and 15 km2 in Kachchh. Movements were located mostly within protected enclosures that corroborate the recommendation of National Bustard Recovery Plans that enclosures of 10-20 km2 can accommodate the birds’ ecological needs to a great extent, if they are managed scientifically. This action supplemented with power line mitigation in the areas surrounding enclosures is necessary to restore potential habitats across the species’ range, wherever feasible. The National Lesser Florican survey was jointly conducted by the project team with partner agencies in July - September 2018 that yielded an estimate of 426 (174–805 95% CI) male territories (conservatively 220 + 38) across the range; highlighting the critical status of this species for urgent conservation efforts. Investigation on patterns of bird community structure in relation to land-use driven habitat changes in the arid grasslands of Thar suggested that although primary 2 grassland habitat is essential to save the full spectrum of the regional species pool, low-impact land-uses can act as important secondary habitats for conservation of bird species. Assessment of factors that shape vegetation in the arid zone of India in Thar, Jaisalmer showed a 62% loss in the vegetation types to agriculture and settlements highlighting the need to delineate conservation areas based on requirements of faunal species of interest and its habitat requirements before a complete wipe-out of vegetation structure types occur. Molecular analysis of GIB biological samples revealed that genetic differentiation between GIB subpopulations was low to moderate and level of gene flow between Rajasthan and Gujarat subpopulations was high. From bird carcass surveys under power lines in Kachchh, we estimated carcass encounter rates of 0.27 (0.14 SE) and 0.25 (0.06 SE) per km per month for high- and low- tension power-lines and mortalities of ~22,000 birds (all species) annually in ~1100 km2 GIB habitat emphasizing the need for immediate power line mitigation measures. Preliminary investigation of soil and GIB food samples revealed presence of organophosphate pesticides in GIB habitat in and around Rollapadu Wildlife Sanctuary, Andhra Pradesh. 3. As part of social engagement, our team surveyed villages in Jaisalmer district to assess livelihood concerns and conservation attitude of the local population. We intend to involve the locals as stakeholders in GIB conservation to create goodwill, and these social surveys will help in developing outreach programs. Additionally, customized nature education programmes in 22 schools, skill development workshop for responsible nature tourism to local youth and forest department staff, awareness program to sensitize locals and tourists on grassland and GIB conservation at Desert festival, Jaisalmer were conducted. Publicity materials such as posters, tshirts, caps, books, bags, brochures for power agencies and other stakeholders were prepared and widely disseminated. The team met with representatives of various private and government power agencies as well as senior government officials, media and legal fraternity to sensitize them on the critical issue of power line mitigation for GIB conservation. We also conducted training workshops on population, habitat and threat surveys involving Forest Department staff and volunteers in bustard range states. 4. Under pilot habitat management, 801 dogs from 23 villages in/around DNP were sterilized in collaboration with Humane Society International (HSI)- India and Rajasthan Forest Department. Analysis of data collected from population surveys of dogs and other nest predators in/around DNP is under progress. Preliminary analysis showed that the proportion of unsterilized dogs is still very high in villages. Pigs and desert foxes were the most abundant nest predators in/around DNP. Preparations are underway to relocate nest predators from GIB breeding enclosures in DNP. Meetings with the local community to manage a portion of their land in GIB-friendly manner, and interactions with power agencies and bird diverter suppliers for marking critical power lines were held. More bird diverters for power lines have been procured for installation with the help of power agencies in Thar.