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Item An Ecological assessment of Baan Ganga wetland, Uttaranchal(Uttaranchal Forest Department and Wildlife Institute of India, 2006) Rawat, G.S.; Pandav, Bivash; Mathur, V.B.; Sankar, K.; Hussain, S.A.; Adhikari, B.S.; Sinha, B.C.; Pandav, Bivash; Sivakumar, K.; Padalia, H.; Chaturvedi, R.K.; Babu, M.M.An Ecological Survey of Baan Ganga Wetlands in Haridwar Forest Division, Uttaranchal was conducted during January to November 2006 by a team of faculty and researchers from the Wildlife Institute of India (WII) Dehra Dun. The study components include rapid assessment of the flora, fauna (mammals, birds and fishes), water and soil quality of the area, mapping of the conservation reserve and designing of interpretive facility for the wetland. 2. Baan Ganga wetland represents a remnant Terai habitat in Uttranchal. Occurrence of endangered swamp deer and a variety of floral and faunal communities typical of Terai habitat amidst human dominated landscape warrants careful co-management approach. A total of 178 plant species were recorded from the Baan Ganga wetlands. Of these, 40 species were hydrophytic, 122 species semi-aquatic and 117 mesophytic. Detailed list of the flora along with their habitat and photographic records have been provided. 3. The survey area faces heavy anthropogenic pressures including heavy livestock grazing, fishing, pollution from the untreated sugar mill effluents, cutting and burning of natural vegetation and agricultural encroachment. Despite several pressures the area continues to attract a variety of wetland birds and has tremendous opportunity for developing a popular eco-tourist destination and thereby creating new opportunities in education, recreation, eco-tourism and research in the area. 4. Based on the rapid ecological surveys on various aspects, following major recommendations are given for the conservation and management of the Baan Ganga area: (i) Maintenance of stream flow all through the year (ii) Traditional fishing as in practice at preset may be continued (iii) Initiate a project to promote aquaculture (iv) Initiate conservation awareness programme for the local people especially about the adverse impact of pesticide use in the agriculture fields around the Baan Ganga. There should be a check on the release of effluents from the industries which are located on the upstream areas. Effluents must be treated before releasing into the natural system (v) Maintain heterogeneity in vegetation types. Aquatic weeds are required to be managed properly in year-wise plan. There should not be any construction along the banks of river which will change the hydrological system hence there will be change in the vegetation types. Cattle grazing needs to be regulated and a proper rotational grazing system needs to be implemented in consultation with the local communities (vi) Control of water hyacinth by utilizing this species as a compost / green manure (vii) Regulate exploitation of Phragmites and Typha and (viii) Develop an interpretation centre highlighting the biological and conservation significance of this area for development of eco-tourism.Item A quantitative analysis of incidental capture of seaturtles and mortalities during commmercial shrimp trawling along the coastal waters of Orissa(Wildlife Institute of India, Dehradun, 2002) Gopi, G.V.; Pandav, Bivash; Choudhury, B.C.This study aimed to assess the efficiency of TED in reducing the mortality rate of sea turtles, with a view to lobby for the introduction and promotion of this approach in trawl nets in India. The aim was also to provide a realistic cost benefit analysis in terms of the economic loss to the fishing agencies on using the TED.Item Monitoring tiger and its prey in Chilla range, Rajaji National Park, Uttaranchal, India(Wildlife Institute of India, Dehradun, 2006) Harihar, Abhishek; Pandav, Bivash; Goyal, S.P.The Rajaji National Park along with the adjoining Corbett Tiger Reserve forms the north-western limit for the distribution of the Tiger and Elephant in the Indian Subcontinent. Most parts of this landscape are under anthropogenic influence. Following the notification of the earlier sanctuaries (Rajaji, Motichur & Chilla) to a National Park (Rajaji National Park) in 1983, voluntary relocation of human (Gujjar community) settlements is underway (since 2002). The Chilla Range of Rajaji National Park is presently void of human settlements (Gujjars) and is showing very healthy resurgence of vegetation indicating promising signs of recovery with respect to utilization of the area by wildlife. This study carried out across two years (2004- 2005 to 2005-2006) aimed at monitoring the tiger population within Chilla range following a human resettlement program. Photographic capture-recapture analysis (450 trap nights each year) was used to estimate the density of tigers. Ecological density of wild ungulate prey species was estimated using line transects in conjunction with distance sampling. A total of nine permanent transects were laid and sampled eight times each, every year (102.8 km of walk each year). Food habits of tiger were determined by analysing field collected scats. Our results indicated that Chilla range supports a high ungulate prey density (76.5 individuals km-2 in 2005; 70.98 individuals km-2 in 2006) and has the highest reported sambar density (25.67 individuals km-2 in 2005; 24.69 individuals km-2 in 2006). Though we photographed 12 different individuals during our study (2004-06), the tiger density was found to be low (3.01 tigers 100km-2 in 2005; 2.54 tigers 100km-2 in 2006). The current wild prey biomass off take by tigers was estimated to be 2.78%. However, a predicted ~14 tigers 100km-2 can be supported within Chilla range given a 10% biomass off take (following the model developed by Karanth et al., 2004b). Past anthropogenic pressures have probably caused a downward trend in the tiger densities. From the photographs obtained during this study, it is clear that tigers are breeding in Chilla range. Given adequate protection Chilla can serve as a major source population from where tigers will breed and disperse into neighbouring forests within the Shivalik landscape. A continuous monitoring program is envisaged to document this recovery of predators, prey and their habitatItem 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 Ecological Assessment of Siswan Reserve, Punjab(Wildlife Institute of India, Dehradun, 2017) Bhardwaj, A.K.; Srivastav, A.; Pandav, Bivash; Singh, Pratap; Adhikari, B.S.; Uniyal, V.P.; Badola, R.; Das, A.This study was undertaken with the following objectives: (i) Generate floral and faunal baseline information. (ii) Understand mutual linkages and issues, between local communities and the reserve (iii) Sensitize the local staff about ecological importance of this area and its attributes rapid surveys were carried out by a team of WII faculty and researchers for various taxa from October 2016 to June 2017. Surveys were carried out for generating information about large mammals, birds, reptiles, amphibians, insects and vegetation. To assess peoples perspective concerning the reserve participatory methods of focused group discussions (FGDs), social and resource mapping and time line surveys were undertaken. Visits for various rapid assessments were made more productive by conducting capacity building exercises for department staff simultaneouslyItem Trichotaxonomy of tiger prey from Terai Arc landscape, India: A comprehensive manual(Wildlife Institute of India, Dehradun, 2024) Kumar, Shrewshree; Biswas, Suvankar; Pandav, Bivash; Mondal, SamratThis manual deals with the systematic protocol in identification of prey species from the feces of tiger collected across the Indian part of the Terai-Arc landscape, using morphological techniques. It presents the microphotographs of the undigested hair of various prey species in different resolution for easy and unambiguous identification for other researchers working in this field.