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    Assessent of prey populations for lion re-introduction in Kuno wildlife sanctuary, Central India
    (Wildlife Institute of India, Dehradun, 2005) Johnsingh, A.J.T.; Qureshi, Q.; Goyal, S.P.
    Realizing that it is unwise to keep the only free-ranging population of Asiatic lions (Panthera leo persica) in one location (Gir forests), the Government of India made an effort to establish the second population in Chandraprabha Wildlife Sanctuary (WLS, 96 km2), Uttar Pradesh, in 1957. This effort, for various reasons, did not succeed. In 1993-94, with the aim of finding a second home for the lions, a team from Wildlife Institute of India (WI!) surveyed three wildlife habitats in the states of Rajasthan and Madhya Pradesh. Among the three, Kuno WLS (345 km2) was identified as the most suitable site. With assistance from the Government of India, a twenty-year project was initiated in 1995, to establish a disturbance-free habitat here for reintroducing lions. Between 1996 and 200 I, twenty-four villages, with about 1547 families, have been translocated from the Sanctuary by the Madhya Pradesh Forest Department. The Madhya Pradesh Government has also demarcated a 1280 km2 Kuno Wildlife Division, encompassing the Sironi, Agra and Morawan forest ranges around the Sanctuary. In order to assess whether the Sanctuary has sufficient wild prey base, the WII was requested to asses the availability of prey in early 2005. With the assistance of34 forest staff 17 transects totaling 461 km were surveyed over an area of 280 km2 The density of catchable wild prey (chital, sam bar, nilgai, wild pig) by lions was 13 animals!km2. There are about 2500 cattle, left behind by the translocated people which are considered to be the buffer prey for lions to tide over the likely problem of drought periodically killing wild ungulates. With the implementation of the recommendations such as the control of poaching, grassland management, building rubble wall around the Division and water augmentation, we predict a substantial rise (ca.20 animals!km2) in the wild prey base for lions by end of2007. This prey density would be able to support the first batch of five lions (three females and two males) to be reintroduced in the beginning of 2008. Even if all the three females raise cubs, there will be sufficient wild prey by the end of 2009 to support them. Meanwhile efforts should be made to implement all the recommendations given in this report with immediate effect and get the whole hearted support of Gujrat Government to make this historic venture a success.
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    Conservation status of tiger and associated species in the Terai Arc Landscape, India
    (Wildlife Institute of India, Dehradun, 2004) Johnsingh, A.J.T.; Ramesh, K.; Qureshi, Q.; David, A.; Goyal, S.P.; Rawat, G.S.; Rajapandian, K.; Prasad, S.
    The Indian portion of Terai Arc Landscape (TAL), stretching from Yamuna river in the west to Valmiki Tiger Reserve, Bihar in the east, spreads across five states along the Shivaliks and Gangetic plains. This unique Landscape consists of two distinct zones: (i) bhabar, characterized by a hilly terrain with course alluvium and boulders, and sal mixed & miscellaneous vegetation communities and (ii) terai, characterized by fine alluvium and clay rich swamps dominated by a mosaic of tall grasslands and sal forests. The terai, in particular, is listed among the globally important 200 ecoregions for its unique large mammal assemblage. Over the decades as a result of conquest of malaria, establishment of numerous settlements and consequent increase in human population, this Landscape has become highly fragmented and degraded. This has led to the local extinction of species such as one-horned rhinoceros (Rhinoceros unicornis), swamp deer (Cervus duvauceli) and hog deer (Axis porcinus), for example, west of Sharda river. Despite its ecological richness and faster rate of degradation and species extinction, conservation initiatives are far from desired in this Landscape, perhaps due to inadequate information and lack of coordinated efforts. Given this circumstance, the Wildlife Institute of India (WII) submitted a proposal to Save the Tiger Fund (National Fish and Wildlife Foundation, USA) to carry out a survey of TAL on the Indian side, which is ca. 42,700km2 with a forest area of ca. 15,000 km2. Save the Tiger Fund allotted US $53,500 and an 18-month project was initiated in July 2002. The project objectives were to (i) develop spatial data base on the TAL, (ii) assess tiger (Panthera tigris) and large ungulate distribution and status, (iii) describe the status of the Landscape and its vegetation characteristics and (iv) document the socioeconomic conditions of the local people and major disturbance factors. Indian Remote Sensing (1C/1D) satellite images with the spatial resolution of 188m (WiFS) and 23.5m (LISS III) pixel sizes, and Survey of India topographic maps were used for habitat mapping and other spatial database. The study team surveyed the entire Landscape twice between October 2002 and June 2003 for assessing the status of tiger and other associated large mammal species, and habitat conditions. Extensive sampling of 246 foot transects covering 1001.2km and 1530 circular plots, with nested design, were carried out across the TAL. Demographic and socioeconomic profiles of people were derived primarily from the raw data of 1991 Census. Owing to the applied nature of the project, it was decided to hold a two-day workshop to share the findings and to attain synergy among Forest Officials, NGOs and other conservation agencies for implementation in the field. The study revealed that the TAL contains homogenous vegetation communities of eight broad types, but the structural components vary highly across the Landscape. The tiger habitats on the Indian side are in nine blocks (referred as Tiger Habitat Blocks, THB) and the largest block (ca. 4,000 km2) is around Corbett TR. The forests in Kalsi, Dehradun and Haridwar Forest Divisions in Uttaranchal and Bijnor Plantation Division, Bahraich and Shrawasti Forest Divisions in Uttar Pradesh were devoid of tiger. Thirteen corridors that potentially connect these nine blocks have been identified. When connectivity with the Nepal side is taken into account, the nine THBs can be pooled into five larger units (referred as Tiger Units, TU). Among these, TU II, which is in the bhabar tract and includes Corbett TR, is the most intact one. TU IV (Pilibhit FD-Suklaphanta Reserve-Kishanpur WLS-Dudhwa NP- Bardia NP-Katernighat WLS) is the most extensive terai habitat. Each piece of habitat and connectivity in these Units are crucial and at the same time, are threatened by anthropogenic pressures. Ungulate distribution and relative abundance in TAL corresponds to the high variation or heterogeneity in habitat features. However, the overall status of prey (ungulate) availability is reasonably better in this Landscape, largely owing to the interspersion of Protected Areas between Reserve Forests. The evidence is clear that tiger distribution and its abundance are linearly related to wild ungulate prey such as chital (Axis axis) that has wider spatial distribution. Sambar (Cervus unicolor) and wild pig (Sus scrofa) also contribute substantially in deciding the occurrence of tiger in bhabar and terai regions respectively. The domestic dog was identified as a reliable indicator of disturbance that impedes tiger occurrence. Undisturbed hilly (bhabar) areas such as Corbett TR, which usually have many deep nallahs, providing hideouts and abundant prey (sambar, chital and wild pig) support substantial population of tiger. The terai tall grass habitats, which provide adequate cover, as in Kishanpur WLS and Dudhwa NP, with prey such as chital, pig and swamp deer, is the second best. It appears that in a few years time, tigers may cease to exist in habitats like Sohagibarwa-west (THB VIII), an isolated habitat patch in Uttar Pradesh, which is under enormous anthropogenic pressures. Leopards tend to avoid terai habitats and high-density tiger areas, but are still common in areas extirpated of tiger. Data from the Census of India 1991, for 33 tehsils (units of District) within the study area, indicated that the bhabar, largely west of Sharda river, had significantly lower human density (334/km2) and higher percentage of forest cover (36%). The corresponding figures for terai (east of Sharda river) are 436/km2 and 17% respectively. It appears that the bhabar areas, at present, are in a better position to buffer firewood dependency of the people. Human population increase, ever growing habitat encroachments, poaching, firewood extraction and bhabar grass (Eulaliopsis binata) collection for rope making, stealing of tiger and leopard kills, and boulder mining causing enormous disturbances and fragmentation are the major problems identified. The extensive empirical information (distribution and abundance) collected on vegetation parameters, ungulates and tiger can be used as baseline data to initiate monitoring programmes. In addition, the monitoring should include establishment of adequate number of one-hectare plots and line transects for periodic evaluation of habitat conditions and prey abundance respectively. The study recommends that Chilla-Motichur and Gola river corridors should be established on priority basis and the conservation status of THB IV containing Suklaphanta Wildlife Reserve-Pilibhit FD-Kishanpur WLS should be strengthened. If done, the former will constitute the largest (ca. 8000km2) tiger and elephant habitat anywhere along the foothills of the Himalaya and the latter will ensure the future of one of the finest terai habitats (ca. 1200km2). Initiation of a conservation programme like establishing Rajaji-Shivalik Tiger Reserve is urgently needed to eliminate boulder mining in Yamuna river to ensure the ranging and occurrence of tigers between Shivalik FD and the Kalesar-Simbalbara forests, the western most limit of tiger distribution range. Raising of fuel wood plantations with community participation, use of fuel-efficient chulas, resettling of gujjars (migratory pastoralists) and eight key villages, shifting of one factory and weaning people from bhabar grass collection and conservation education programmes are also recommended. There was a consensus in the two-day workshop held on 6-7 November 2003 in WII that the Nepal model, with a strong scientific foundation and involvement of local people, needs to be adapted for the Indian side of TAL. Cross border cooperation between India and Nepal is a must to ensure the long-term conservation of tiger and its habitat in this Landscape
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    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 habitat
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    Evaluation of the functional status and quality of corridors connecting fragmented populations of tiger in the Indian part of Terai Arc landscape : Final Technical report
    (Wildlife Institute of India, Dehradun, 2010) Rajapandian, K.; Anwar, M.; Goyal, S.P.
    Most rare and critically endangered species such as tiger (Panthera tigris) exist in human dominated landscapes as small, fragmented and isolated populations in most part of its range. A prerequisite for conservation efforts and management is to identify the factors which affect the distribution and abundance of the species of interest and connectivity between populations occupying the remaining fragments. Tiger populations have dramatically declined in recent years in the Indian part of Terai Arc Landscape (TAL). This top priority landscape for tiger conservation was once continuous across the Himalayan foothills but is now highly fragmented and most of the remaining large, intact habitats are located within protected areas. As tigers cannot sustain viable populations in small habitat fragments, an assessment of potential suitable habitat and connectivity among the remaining habitat patches is required to assess possibilities to ensure the creation of a single functioning metapopulation unit for tiger. Therefore, there is a need to monitor condition of tiger’s habitat (Smith et al. 1998). The effectiveness of potential corridors depends on the quality of habitat with in the corridor, the matrix that surrounds the corridor and redundancy of the corridor network (Collinge, 1998; Haddad et al. 2003). Out of ten corridors identified in TAL (Johnsingh et al., 2004), seven corridors were taken on priority basis for understanding quality and functionality assessment. Five and two corridors exist in Uttarakhand and Uttar Pradesh state of India, respectively. In view of understanding functionality of corridor, the objectives of this study was aimed (i) To describe the functional status (use and intensity) of the corridors with reference to tiger, (ii) To study the biological characteristics (vegetation composition, prey distribution and abundance, and disturbance status) that determines the corridor quality and (iii) To use, and to document the socioeconomic issues affecting the corridor existence and its use. Under this study, we describe basic data obtained for these seven corridors for their habitat characteristics, use by tiger and level of disturbance under Part I. This would provide base line information for comparison in future. Data analysis undertaken in Part II of this report are use of ecological modeling models to assess functionality of these corridors using remote sensing data and other aspects
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    Study of genetic diversity in wild (Sus scrofa cristatus) and domestic (Sus scrofa domestica) pig to find level of hybridization between them in the vicinity of Ranthambhore National Park
    (Wildlife Institute of India, Dehradun, 2015) Pandey, P.; Nigam, P.; Chauhan, N.P.S.; Goyal, S.P.
    Wild pig (Sus scrofa cristatus) has a wide geographical range among all ungulates and terrestrial mammals found in the Indian subcontinent and forms an important prey-base for carnivores. Despite the variation with domestic pig in chromosome numbers, these animals can mate and produce fertile hybrids that have physical attributes similar to wild pig. A systematic study on wild pigs by the Wildlife Institute of India in Ranthambhore National Park revealed that wild pigs stray out of national park, raid agricultural crops and utilises the agro-ecosystem in peripheral villages for food resource and shelter and thus coming in contact of domestic pigs. As a result, there may be genetic hybridization between the wild and domestic pig populations. Hybridization between wild and domestic pigs may lead to introgression of alien alleles that can affect the genetic fitness and overall immune response. Thus in order to detect the hybridization and to quantify the impact on wild species, genetic assessment of wild and domestic pig is necessary with ultimate goal to find out extent of hybridization if any. Therefore, a study on genetic assessment of wild and domestic pigs and to evaluate the use and efficacy of power fence in controlling crop damage caused by wild pigs as advised by the Training, Research and Academic Council (TRAC) was undertaken from 04.02.2012 to 03.08.2014 around Ranthambhore National Park. The objectives of the study were (a) To study genetic diversity in wild and domestic pigs in the vicinity of Ranthambhore National park, (b) To find the level of hybridization between wild and domestic pigs based on genetic variability, (c) To evaluate the use and efficacy of power fence in controlling crop damage caused by wild pigs, (d) to evaluate the use and efficacy of power fence in controlling crop damage caused by wild pigs and (e) Based on the findings of the project, examine the possibility of hybridization between wild and domestic pigs in other parts of the country for further study. In view of this, report has been in two parts i.e. Section –I describes the genetic assessment of wild and domestic pigs where as Section II is related to use and efficacy of power fence. We systematically collected the biological samples of unrelated domestic pigs (n=65) from different villages surrounding the Ranthambhore National Park as a zone of interaction and also from different parts of Sawai Madhopur city as a control. For the genetic characterization and detection of event of introgression in wild pigs, we proposed collection of 30-40 blood samples in the project. The habituation of animals on baits could not been successful in spite of best efforts. This was due to the delayed receipt of permission to capture animals, in appropriate weather conditions making habituation procedure difficult and unsuccessful capture. In view of this, we collected other samples of wild pigs such as hair and faecal matter to meet the objectives of the project as these samples are equally amenable for genetic analysis but require appropriate optimization of protocols. Thus we collected blood samples (n=6) of unrelated wild pigs representing Ranthambhore National Park. Apart from blood samples, we also collected wild pigs faecal (n=26) and hair samples (n=34). For genetic diversity and detection of event of introgression, we amplified partial fragment (662 base pairs) of control region from mitochondrial genome (Asch et al., 2011) and a panel of 10 highly polymorphic microsatellite markers in domestic (n=55) and wild pig samples (n=66). We tested the applicability non-invasive faecal and hair samples for genetic assessment and evaluation of genetic introgression. Faecal DNA was of low molecular weight with PCR success rate restricted up to 200 base pair of mitochondrial DNA. We found PCI and Qiagen kit protocol for DNA extraction better for hair DNA extraction. As reported in the literature for PCR success (40 to 80%) in using such samples, our success rate in pig samples (hair and a faecal matter) was also between 60 and 90% whereas it was possible to obtain good quality data with all blood samples. Hence, collection of adequate invasive samples at large landscape would be difficult, therefore, we suggest use of non-invasive samples i.e. faecal matter and hair in future studies. Optimized protocols undertaken in this study for using noninvasive samples would have immense advantage for undertaking future cost effective studies on wild pigs. First time we report presence of two haplotypes with one segregation site in 560 base pair of amplified sequence of control region in eastern most population of wild pigs. Two haplotypes (WP_Hap-1 and WP_Hap-2) were shared equally i.e. 50% each in the population. The overall haplotype diversity of wild pigs was found 0.6 ± 0.13 whereas the nucleotide diversity was 0.001. In total 13 haplotypes with 24 segregation sites were recorded in 590 base pair of amplified sequences of domestic pigs. Two haplotype (Hap-1 and Hap-9) were shared by 80% of domestic pigs examined so far. Seven haplotype were detected only once (DP_Hap-3, DP_Hap-5, DP_Hap-8, DP_Hap-10, DP_Hap-11, DP_Hap-12 and DP_Hap-13) indicating their different geographic origin. The overall haplotype diversity of domestic pigs was found 0.79 ± 0.04 whereas the nucleotide diversity was 0.01. We selected eleven microsatellite markers for genotyping purposes. Of total samples (n=66), it has been possible to generate data complete data on multi locus genotyping only for 22 and were used for introgression purposes. Out of the eleven microsatellite markers tested on domestic and wild pig samples, three loci (S0090, S0026 and SW72) deviated from HWE whereas SW72 also showed presence of null alleles in domestic pigs. Six loci (SW122, SW24, S0090, 0225, S0226 and SW911) deviated from HWE whereas none of the loci showed sign of null alleles in wild pig samples analyzed. We found overall high genetic diversity in domestics pigs (Na=14.2, Ho=0.72 and He=0.86) as compared to the analyzed wild pig samples (Na=3.2, Ho=0.7 and He=0.7). We did not find any common haplotype between individuals of wild and domestic pigs and thus the introgression at mitochondrial level can be ruled out in the analyzed samples. We analyzed microsatellite marker data of both domestic and wild pig samples. By using Bayesian MCMC approach implemented in Structure 2.3.1. indicated admixed nature (ca.55%) of the wild pig samples. Similar results were also observed during factorial component analysis (FCA) where the wild pig individuals showed more affinity towards domestic pigs. Thus we report first time the presence of hybrid wild pig individuals (wild at mitochondrial level and domestic at nuclear level) in RTR. Therefore, absence of mitochondrial genetic introgression and presence of nuclear genetic introgression suggests unidirectional hybridization. Section II, describes the use and efficacy of power fence which was evaluated in controlling crop damage caused by wild pigs. Traditionally, wild pigs have been kept out of cultivations by scaring them away or restricting them with barriers. Scaring wild pigs with flash lights, fire, fire-crackers, crop protection guns, stone slings etc may effectively deter them sometimes. Most forms of effective barriers for wildlife such as trenches, rubble wall or conventional fences, are expensive to construct and maintain. A power fence is purely a psychological barrier. Power fence is a relatively new control technique and not fatal for animals and only restricts their movements. Power fencing is most effective and safe to animals and to humans. If properly constructed and maintained, it can effectively keep most of the animals out. Power fencing system provides an economic and a practical solution to achieve maximum protection through effective control of animal trespass. In this study, we developed the pig-proof power fences by construction of fence line around the crop fields in Jaitpur village situated on the boundary of Ranthambhore National Park, and evaluated their efficacy in reducing crop damage. We compared the extent of wild pig crop-raiding in the fenced and adjacent unfenced areas. The power unit had a solar panel, a 12 volt power battery, and an energizer to provide current to 1.5 km length of the two fences. We erected the electric fence as per the designs specified in June 2006 under different project when the fields were prepared for sowing crops. A fence design with posts at an interval of 8 meters and GI wires at the height 15, 37.5, 62.5, 100 and 135 cm were tested. Another design with posts at an interval of 8 meters and GI wires at the height 15, 37.5, 62.5, 100, 135, 165,195 and 225 cm was also constructed. The pig-proof fence was 4.5 feet in height with five strands; the first and third strands were connected to earthing, and the rest three i.e. 2nd, 4th and 5th strands were live strands. The pig and nilgai proof fence line was constructed along the forest boundary and crop fields, and it was 8.5 feet in height with 8 strands. The 1st, 3rd and 5th strands were connected to earthing system, and the rest five strands i.e. 2nd, 4th, 6th, 7th and 8th were live wires. The fences were monitored regularly by walking along the perimeter to evaluate their effectiveness and we discuss our findings . Both the fences were maintained properly. We recorded high range of voltage (7.9- 8.1 KV) at the energizer point. Average output voltage of the main fence i.e. nilgai-pig pro offence ranged from 5.5 to 6.5 KV. The voltage of small pig-proof fence was slightly on the lower side i.e. 5.2 to 6 KV. The voltage at 1000m fence length was higher than at shorter distances, which might be due to good earthing system. Overall the fences were found effective against pigs and nilgai. We conclude that the present study support the ecological finding (of previous project of WII) about genetic introgression between wild and domestic pigs around Ranthambhore National Park. This study provides valuable information on the genetic structure of indigenous wild pig which would be useful for future conservation program. Wild pig in RTR is in a vulnerable state as a distinct genetic wild resource and we suggest for appropriate measures to be undertaken to minimize the contact zone between wild and domestic pigs in and around RTR by using appropriate physical barriers as designed and tested for its efficacy. This may enable to restore genetic diversity of wild pigs after few generation through back crossing with wild pigs. We also suggest there is a need to re-visit the study in RTR with using optimized protocols to document spatial distribution of hybrids using NGS (hair and fecal matter) for developing appropriate strategies of wild pig genetic resource adapted to hot climatic conditions (Estimated expenditure would be Rs.6.0 lakhs/year). In view of valuable wild pig genetic resource for human being, there is a need to assess extent of introgression from domestic to wild pig populations of different bioclimatic zones. We also suggest for use of both mtDNA and nuclear markers which avoids inheritance bias because they detect information on both the maternally and codominatly inherited regions
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    Current population status, distribution and threats to Indian Pangolin (Manis crissicaudata) in Terai Arc Landscape, Uttarakhand: a pilot study
    (Wildlife Institute of India, Dehradun, 2020) Lyngdoh, S.; Goyal, S.P.; Nigam, P.; Kumar, V.; Badola, S.; Rasailly, S.
    This 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 Department.