Browsing by Author "Gopi, G.V."

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Aspects of ecology of large carnivores and their prey in and around Dibang Wildlife Sanctuary, Arunachal Pradesh, India.
(Wildlife Institute of India, Dehradun, 2021) Adhikarimayum, Aisho Sharma; Gopi, G.V.
The conservation of large mammalian carnivore is prioritized as it acts as keystone species across diverse zones of habitat around the globe. They play an important role in regulating and maintaining the abundance of ungulates, in turn influencing the functioning of the ecosystem. In the last few decades, large carnivore’s population have been declining due to anthropogenic activities such as habitat destructions creating forest patch, illegal trade and hunting on wildlife. These threats posed a challenge in the conservation and management of large mammalian carnivores. The co-existence of large carnivores is occurring in many places in the wild due to the availability of less prey base, habitat fragmentation and high human interferences. Thus, the understanding of ecology of large carnivore and their prey species particularly on habitat selection, prey-predators’ relations in aspects of distribution and abundance, such ecological data can be useful to evaluate not only their habitat requirement but will also aid in long term management of wildlife and conservation of their habitats. So, efficient conservation and monitoring of large carnivores such as tiger and wild dog (dhole) is required for the assessment of complex mix of ecological, ethical and symbolic inter-relationships. The study was conducted at Dibang Wildlife Sanctuary; it covers an area of 4149 km2 and situated in Dibang Valley district of Arunachal Pradesh. The tiger is culturally considered as a brother by the local Idu Mishmi community who live in the Dibang Valley district in Arunachal Pradesh. Though the local community has long been claiming about the presence of tigers in the region, unfortunately, no efforts were made by the line departments, academicians, or conservationists to assess and monitor the tigers, their prey, and habitat in Dibang Wildlife Sanctuary. This preliminary study was carried out after the rescue of tiger cubs from the district in Angrim Valley during December 2012. The rescued tiger cubs were the first-ever record of a tiger from the sanctuary. The primary objectives for the aspects of ecology of large carnivores and their prey in and around Dibang Wildlife Sanctuary are: a) To estimate the abundance of large carnivores in and around the Dibang Wildlife Sanctuary, b) Assess the abundance of wild prey in and around the Dibang Wildlife Sanctuary, c) Assess the food habits and prey selectivity of large carnivores in and around the Dibang Wildlife Sanctuary, and d) To quantify the extent of human-wildlife interaction in and around the protected area. An intensive camera trapping exercise was carried out during October 2015 to June 2017 in the Dibang Wildlife Sanctuary and adjoining landscapes to monitor large carnivores and their prey species. Dibang Wildlife Sanctuary and its adjoining landscape harbors sizable population of large carnivores such as tiger and wild dogs. The study has reported the first photographic evidence of tiger presence from the community forest of Mishmi hills range in Dibang Valley District at an altitude of 3630 m amsl and it is the highest record from the Indian part of the Eastern Himalaya Biodiversity hotspot. This study has generated baseline information on tiger, wild dog and prey species in Dibang Wildlife Sanctuary and adjoining landscape. Tigers do not necessarily use only the protected areas; they use the community forests outside the protected area as well.
Assessing the distribution and density of the Fishing Cat in Bhitarkanika mangroves of eastern India by
(Wildlife Institute of India, Dehradun, 2024) Ashik, C.S.; Mukherjee, Shomita; Gopi, G.V.; Pandav, Bivash
Identifying the areas of occurrence, population, and the factors affecting the species distribution is critical in conservation and management. The Fishing Cat (Prionailurus viverrinus), a smaller feline native to South and Southeast Asia, is globally vulnerable and adapted to wetland habitats, with a diet primarily consisting of fish. This makes Bhitarkanika, a mangrove ecosystem, an ideal habitat for the Fishing Cat. This study was conducted to estimate the species density, determine the factors affecting its distribution, and assess the effect of lunar illumination and tidal fluctuation on Fishing Cat activity. Despite known occurrences of Fishing Cats in this area, there has been no proper assessment of their population or other ecological studies. Camera traps were deployed in 109 grids, each covering 1km², across a total of 145 km², for 2878 trap nights. Camera trap locations are unbaited, with two cameras used to capture both flanks. Spatially explicit capture-recapture (SECR) was used to estimate the density, resulting in 0.6 ± 0.1 individuals per km². The abundance was also calculated, with an estimate of 99 ± 16 individuals. These density estimates from this study are close to recent high-density estimates for the species. The canopy cover, the width of the creek, canopy cover and the distance to the aquaculture farms significantly influenced the Fishing Cat habitat use, indicating the need for the conservation of natural mangrove habitats and regulation of aquafarms present near the forest. In contrast, the presence of Saltwater Crocodile showed a negative effect on the distribution of Fishing Cats. The Fishing Cats were more active during the brighter nights of the moon phase (μ= 266.783, r= 0.051, p< 0.01) due to better visual detection. The activity was influenced both by the tidal fluctuations in terms of food resources from waterbodies and it is further enhanced by the lunar illumination during the night. Pairwise non-parametric tests showed that the probability distributions of Fishing Cat activity under lunar illumination and tide fluctuation (D= 0.125, p-value = 0.9885 and D= 0.125, p-value= 0.9899) were similar, indicating minimal differences between each probability distribution. This study underscores the importance of protecting the mangrove habitat and controlling aquaculture expansion to ensure Fishing Cat survival in the Bhitarkanika National Park.
Assessing the Efficacy of Select Physical Barriers in Mitigating Human-Elephant Conflict in the Human-Elephant Shared Landscape of Golaghat District, Assam
(Wildlife Institute of India, Dehradun, 2021) Das, Gitima; Gopi, G.V.
Human-Elephant Conflict (hereafter “HEC”) is one of the most challenging issues both for elephant conservation and people’s wellbeing in the elephant landscapes. Management of which becomes extremely difficult without the implementation of appropriate mitigation measures. Physical barriers, like solar fences, elephant-proof trenches, stone, or rubble walls are installed as mitigation measures in all elephant-occupied habitats at the edge of the forest and human-use areas, globally. However, installations of the same without a proper scientific rationale and assessing and analysing their site-specific efficacy in reducing elephant incursion in the human settlement areas often fail in doing its intended objectives. It is important to note that humans are also a crucial component of conflict, hence research focusing on social aspects are essential for finding solutions. Keeping such concepts in mind, an assessment to determine the efficiency of two types of physical barriers, viz., solar fence and elephant-proof trench (EPT) was carried out in one of the prime elephant habitats of north-eastern India, in Golaghat district of Assam. Located on the southern bank of the Brahmaputra and home to Kaziranga National Park (KNP) on the west and Nambor-Doigurung Wildlife Sanctuary (NDWLS) in the south, Golaghat offers an ideal site for such study. It is realized that even after the presence of barriers in various areas of the district, conflict cases in the form of crop-raiding, human mortalities and human deaths continue to be reported. Handful studies on barriers and their effectiveness were done recently on the northern bank of Brahmaputra. However, no such appraisal on efficiency of barriers has been done in this landscape, where conflict levels are high. Hence, this study attempted to fill these existing research gaps.
Assessing the Patterns of Human-Wildlife Compensation Around Pakke Tiger Reserve Arunachal Pradesh
(Wildlife Institute of India, Dehradun, 2019) Langlang, Luxmi; Das, Abjijit; Gopi, G.V.
Of all the types of interactions between humans and wildlife, human-wildlife conflict (hereafter HWC) poses a significant challenge to conservation efforts and species survival. This conflict may be manifested with a range of interactions with more negative actions being killing and injury to wildlife and humans while more neutral actions being internalizing costs of living with wildlife. People living in and around protected areas interact closely with wildlife. The negative interaction may be in the form of crop raiding, livestock depredation, property damage or death and injury to human. Thus, such interactions may result in economic loss to people and may create animosity against conservation through reduced public support and retaliatory killing. Further peoples’ perceptions towards HWC may vary by species, especially as large and potentially dangerous animals such as tigers and elephants are seen as a threat to farmers’ livelihoods. In this context, I assessed the patterns of HWC around Pakke Tiger Reserve to identify conflict species and hotspots of conflict. I tried to understand the constraints about compensation in terms of the gap between self-reported conflict and conflict reported to forest department. I also focussed on understanding the perception of people towards commonly found wildlife in the reserve with the help of attitude score. My study was carried out in 41 villages where I interviewed 327 households around Pakke Tiger Reserve. I used a semi-structured questionnaire and open-ended questions to understand the pattern of conflict, compensation issues, attitude towards different species and mitigation strategies most commonly used. Perception data was also collected. Crop damage (mostly by wild pigs, macaques and rodents) was reported as the most prevalent type of conflict around PTR followed by livestock depredation (mainly by wild dogs, tigers and leopards). Property damage and human death and injuries were reported to a lesser extent. Twelve different mitigation strategies were commonly used against crop raiding and livestock depredation. Night patrols and sound were used to keep animals away from fields. Livestock’s were mostly grazed in the forest, and hunting of predators was the most common mitigation strategy against livestock depredation.
Avian Responses to Varying Landscape Parameters in Mangrove Forests of Coastal Gujarat
(Wildlife Institute of India, Dehradun, 2015) Kulkadia, Devanshi; Talukdar, G.; Gopi, G.V.; Sivakumar, K.
Mangrove systems are the most productive ecosystems on the earth. The mangrove environment provides living space for dependent biota of more than two thousand species of flora and fauna of resident, semi-resident or migratory wildlife. The conversion of large contiguous tracts of the tropical mangrove forests to smaller patches embedded in a landscape matrix surrounded by human-altered habitats is one of the most serious concerns as it would affect their associated species such as birds, fishes, etc. In this context, this study was carried out aiming at discerning the responses shown by avifauna to varying landscape parameters like the mangrove patch characteristics, the level of disturbance and the structure of mangrove vegetation. Therefore, the abundance and diversity of the avifauna in mangrove forests at twenty selected sites on the coasts of Gujarat were investigated using point count surveys for a period of five months (December 2014-April2015). 2. A total of 98 points were laid across the twenty patches o(mangroves and surveyed twice during winter and summer seasons, respectively. Data were collected from the four replicates of each point during the entire study period. The total area surveyed during the study at these twenty mangrove patches was 47.97sq.km. These patches were ranging from various size classes with the smallest patch of the size of 0.125sq.km to the largest patch size was of 10.49 sq.km and were distributed throughout the coastline of 1650 km long. Habitat correlates such as structural and floristic characteristics of mangroves were quantified for each patch to establish their relationship with avifaunal abundances. 3. Despite recording only 7 species of mangroves in the twenty patches, a wide variety of birds totaling to 119 species were recorded from the mangroves during the two seasons, i.e. winter and summer during the study. 4. From the data collected by the variable-width point counts, the mean density of birds from the patches were calculated to be 6.485/ha in winter and 4.898/ha in summer. The diversity of birds varied across the seasons. A total of 104 species of birds were recorded during the summer season as compared to 117 species of birds in winter season. 5. Large contiguous patches of mangroves were found to be supporting fewer species of birds than the smaller patches. The avian species richness of the smaller fragments were largely governed by the adjoining environment settings (matrix) of the patch. Therefore, the study found that the diversity of the birds was not found to be getting influenced by the area of the patch as the species richness was found to be increasing with the number of the surrounding matrix. 6. It was found that the structural composition of mangroves especially the canopy cover was found influence the bird density and diversity greatly as with the increase in the canopy cover, the bird species diversity and density also increased in a patch. 7. The bird assemblages in the mangroves showed a significant response towards the disturbance. The disturbed patches contained an overlapping mixed composition of the forest birds and open country birds in an equal proportion, whereas the undisturbed patches showed less number of open country birds. 8. Based on the study, it is suggested that the larger sized mangroves patches are important for their ineffable ecological services, therefore, these patches should be protected and conserved. Similarly, the smaller and fragment of mangroves patches are also equally important as they hold a good number of avifauna! species and hence, we have to adopt some strategies to conserve all the remaining – large contiguous and small fragmented patches of the mangroves from further degradation.
Density Distribution and Factors Influencing Sea Stars in Selected Islands of Lakshadweep India
(Wildlife Institute of India, Dehradun, 2013) Jayaram, Sharmila; Hussain, S.A.; Gopi, G.V.; Apte, Deepak
Coral reefs are the most fragile, complex and diverse ecosystem on earth. But recently, they arc under severe threat due to both natural (climate change, storms and disease outbreaks) and anthropogenic factors (overexploitation, coastal developmental activities and pollution). As evident from earlier studies, a major factor causing degradation of coral reefs is due to an asteroid species belonging to phylum Echinodermata which is considered second to storm damage. Thus to analyze the condition in Lakshadweep Islands I assessed the density of asteroids in four Islands of Lakshadweep. It was found that the five species detected belonging to three families (Oreasteridae, Linckiidae and Acanthasteridae) were having varied density across the four islands. Overall density estimates of the asteroids ranged from 0.05(S.E = 0.02) to 0.80(S.E = 0.09) per 250 square meter. The asteroid density was highest in the uninhabited Island named Bangaram. Correspondence Analysis (CCA) showed that major gradients in environmental variables influenced asteroid species distribution. Sample scores on ordination ' axis 1 were strongly correlated with water pH, water depth and dead coral. Out of the three strongly correlated environmental variables pH was found to be the most ecologically important variable that affects the asteroid distribution. Corallivorous asteroid population outbreaks are becoming a boon to the coral reef ecosystem all over the world and contribution of water pH variation of this outbreaks are being studied well. Thus management strategies in Lakshadweep Islands that 'accounts the variation of water pH are required to conserve the coral reef ecosystem.
Effect of habitat characteristics on waterbird diversity along river ganga in Allahabad, Uttar Pradesh
(Wildlife Institute of India, Dehradun, 2017) Kumar, Ankit; Gopi, G.V.; Hussain, S.A.
Riverine floodplains are a mosaic of different habitat available in the riverine area. It is extensively used by an array of flora and fauna. It supports a huge biodiversity by providing habitat as a resource to various taxa. Many waterbird species are directly and indirectly dependent on the riverine floodplains and use riverine habitat at a certain stage in their life cycle. The area also supports a high diversity of wintering waterbirds. Migratory bird takes refuge in the area during the severe winter in their native habitat. Habitat-specific species use different types of habitat present in the riverine floodplain. The riverine system also has an intricate relationship with the humans. Since a long time, these habitats are subjected to overexploitation that affects the natural ecological processes and the functioning of river. Degradations of floodplains of the major rivers of the world by alteration of water flow, encroachment in river islands and collection river bed materials, discharge of urban and industrial effluents, are threatening the biodiversity of rivers and their associated wetlands. The effect due to different levels of the disturbance is unknown on the diversity and abundance of waterbirds. On these lines, I conducted my study focused on identifying what are the habitat characteristics which is affecting the abundance and diversity of waterbirds and what are the anthropogenic factors affecting its diversity and abundance. The study was carried out in Allahabad District of Uttar Pradesh. It is known for the confluence of two major rivers of India, river Ganga, and its tributary river Yamuna
Effect of land use change on the habitat and abundance of Grizzled giant squirrel in and around Srivilliputhur-Meghamalai Tiger reserve, Srivilliputhur Division, Tamil Nadu
(Wildlife Institute of India, Dehradun, 2024) Bevoor, Shilpa; Gopi, G.V.; Kher, Varun; Goyal, S.P.
Human activities, especially energy extraction and food production, have drastically altered the global environment, impacting many wild species. Since 1990, around 420 million hectares of forests have been lost mainly due to agricultural conversion, significantly affecting biodiversity. In biodiversity hotspots like India's Western Ghats, agricultural expansion, monoculture plantations (tea, coffee, rubber), and non-timber forest product harvesting have fragmented protected areas, altered plant communities, disrupted nutrient cycles, and reduced carbon sequestration. While monoculture plantations reduce biodiversity, they can still provide habitats for some threatened species. Wildlife such as nilgai, blackbuck, elephants, and giant squirrels in India have adapted to these altered landscapes for food, water, and shelter, demonstrating resilience amidst habitat changes. This study focuses on the impact of converting barren lands into mango and coconut plantations around the Srivilliputhur-Megamalai Tiger Reserve in southern India on the grizzled giant squirrel population and habitat. Over the past three decades, these changes have enhanced connectivity between natural forests and agricultural areas, offering energy-rich fruits that attract wildlife, including GGS. This shift has altered ecological dynamics, making wildlife more reliant on cultivated foods and affecting their movement patterns. Density estimates reveal higher concentrations of GGS and nesting sites (dreys) in plantations compared to protected areas, with mixed plantations showing the highest densities due to the availability of nesting sites and year-round fruiting trees. Seasonal variations in GGS distribution highlight preferences for specific tree species based on fruit availability and habitat characteristics. The study also examines drey site preferences, noting GGS preference for mango trees in plantations over coconut trees due to structural attributes that provide better support and protection. These findings underscore the species' adaptation to plantation environments while emphasizing the critical role of specific habitat features for nesting and overall habitat suitability. Local farmers report conflicts with GGS due to crop damage, particularly affecting coconut, mango, tamarind, and other fruit-bearing trees. Perceived economic losses from GGS feeding habits often exceed actual damage levels, emphasizing the need for accurate assessment and targeted mitigation strategies to reduce conflict. Conservation implications stress the importance of maintaining critical habitats within protected areas, establishing buffer zones between plantations and natural forests, and promoting biodiversity-friendly practices in monoculture plantations. Community-based conservation efforts and adaptive management strategies are essential for mitigating human-wildlife conflicts and ensuring the sustainable coexistence of GGS and agricultural livelihoods in this biodiversity hotspot
Effects of Land Use Practices on Diversity and Abundance of Honey Bee Forage Plants in Senapati District, Manipur
(Wildlife Institute of India, Dehradun, 2015) Ziipoa, Benjamin; Rawat, G.S.; Talukdar, G,S.; Gopi, G.V.
North-east India, a global biodiversity hotspot, ·is also known for diverse socio-cultural and land use practices. One of the important cultural practices in a few pocket-s is bee keeping and honey production as a means of livelihood. However, there is a growing concern that with shortening of shifting cultivation cycle and frequent forest fire the diversity of bee forage plants· as well as honey production is declining in the region. Therefore, a study on the diversity of bee forage plants and bee keeping practices was conducted across various land use practices in Purul subdivision of Manipur, North-east India. The objectives of the study were: (i) To quantify the diversity and abundance bee forage plants in different land use land cover types, (ii) To document the honey bee abundance with respect to forage plant availability, bee keeping practices and traditional knowledge among the local bee keepers pertaining to bee keeping. The study was conducted during December April 2015 in Purul and Paomata subdivision of senapati, district, Manipur. The study area was stratified into five land use and land cover (LULC) types: (i) Semi-evergreen (primary) Forests above 1800 m asl; (ii) Moist Deciduous (Open Mixed) Forests between 1200- 1800 m asl; (iii) Secondary forests (Old Thurn Fallows between 1000 - 170q m; (iv) Secondary scrub (Young Thurn Fallows); and (v) Home Gardens and Agricultural Fields. Six trails of 2 km each were laid in various strata. AIthough each trail ten m radius plots were laid to quantify tree species abundance; concentric 5 m radius plots for shrubs and climbers; and four 0.5 m radius circular plots for herbaceous species. Direct and indirect signs of bee nests and locations of bee boxes were recorded. 30 professional bee keepers were interviewed for their knowledge on bee keeping and bee forage plants. Data were analysed following standard phytosociological techniques. Relationship between bee forage plants and bee abundance were established using R3.02 Generalized Linear Model (GLM). A total of 272 species of bee forage plants belonging to 105 genera and 92 families were recorded in the study area. Of these, 84 species were flowering during winter season. The number of flowering bee forage plants increased to 112 during spring season. It was noted that at least 25 species of flowering plants flower almost during all the seasons providing either nectar or pollens to the bees and other insect pollinators. Asteraceae, Rosaceae, Fabaceae, Brassicaceae and Malvaceae were the most dominant species available as bee forage plants, especially in and ar01md home gardens, backyards and cultivable waste. These species were very low in abundance in natural forests. However, Rosaceae and Fabaceae were more Common in Secondary Forests and Old Jhum Fields. Very few species of bee forage plants were flowering in Semi-evergreen Forests during winter seasons. Highest diversity of trees was recorded in semi-evergreen forests followed by Moist Deciduous Forest, Old Jhum Fallow and Young Jhum Fallow. However, overall density was highest in Moist Deciduous Forest. Budleja asiatica, Rubus ellipticus, Pyrlls pahsia, Engelhardtia spicata, Prunus cerasioides, Docynai india were the most widely available flowering species during winter and spring. These species were mostly found in open (Moist Deciduous), Old Jhum Fallows and closer to human habitation. Their frequency, density and distribution pattern has been compared across various land uses. The results revealed that settled agriculture with adequate cover of primary and secondary forests in vicinity coupled with plenty of ornamental plants and vegetables are best land use practices for honey production as well as enriching the pollinator diversity in the area. Short Jhum cycles and resultant frequent fires are detrimental to bees as well as bee forage plants. Pattern of bee distribution, local knowledge on bee keeping and conservation practices in relation to land use practices have been presented and discussed.
Factors Influencing Small Carnivore Community Structure in Chandoli National Park Northern Western Ghats
(Wildlife Institute of India, Dehradun, 2019) Lad, Himanshu C.; Gopi, G.V.
The current study was conducted on small carnivores in Chandoli National Park of Sahyadri Tiger Reserve from December 2018 to April 2019. The main objectives was to understand drivers of spatial distribution and temporal variation amongst sympatric small carnivores present in the study area. This study provided information on local small carnivore distribution, dietary pattern of palm civet and time activity patterns of small carnivores in Chandoli national park
Foraging ecology of Great-Slaty Woodpecker in and around Pawalgarh Conservation reserve in Western Himalaya
(Wildlife Institute of India, Dehradun, 2024) Kaur, Sarabjeet; Gopi, G.V.; Uniyal, V.P.
The Great Slaty Woodpecker (Mulleripicus pulverulentus, Temminck 1826) is an old-world woodpecker that prefers mature and old-growth dipterocarp forests (including Shorea robusta, Sal) across its known distribution range. The study reveals population demography, the social system and foraging behavior from logged forest and infer the distribution and home range of the Great Slaty Woodpecker, a cooperative breeding bird species, in and around the Pawalgarh Conservation Reserve in the western Himalaya of Uttarakhand state. This study presents the first census conducted for the Great Slaty Woodpecker, providing an ecological baseline for the species population estimation from its known distribution range. I inferred the home range size of each group based on 161 independent sightings of 11 family groups. These sightings represent behaviors such as foraging, nesting, roosting, vocalizations, and territory defense
Genetic assessment of the Non-descript pig breeds across selected regions of Uttarakhand
(Wildlife Institute of India, Dehradun, 2023) Sahoo, Khushboo; Gupta, S.K.; Gopi, G.V.
India, which has ancient history of pig rearing, is home to several indigenous pig breeds that reflect the adaptation of Sus scrofa to different environmental and cultural conditions. However, only 13 of these breeds are currently recognized and documented by the National Bureau of Animal Genetic Resources. The present research was undertaken to identify the spatial distribution, socio-economic status, pig husbandry methods of pig rearers, and the impact of Exotic pig breed on the indigenous breed and ecology of the region. As molecular characterization is a valuable tool that provides insights into the evolutionary history and genetic diversity of the current pig breed raise in a region. Hence by incorporating molecular techniques in understanding of the domestic pig breed and their interactions with ecosystems, promote more precise and science-based management that contributes to biodiversity conservation and sustainable husbandry practices. The present study will also aim to evaluate the maternal lineage, genetic diversity and population structure of the domestic pig breeds at the regional scale, using microsatellite markers and mitochondrial DNA sequences. The survey and sampling was done in the planar (Dehradun, Haridwar and Nainital) districts of Uttarakhand, a mountainous state of India that lies in the foothills of Himalayas, where rapid urbanisation and continuous migration make us reconsider the necessity of an organise promotion of the piggery sector due to its multiple ecological implications.
Golden Langur Distribution, Habitat Selection and Corridor – Connectivity: Assessing Patterns and Addressing Threats
(Wildlife Institute of India, Dehradun, 2024) Basumatary, Rishi; Nath, Anukul; Gopi, G.V.; Chetry, Dilip
The Golden Langur (Trachypithecus geei), is an endangered colobine primate, confined to fragmented forest patches in western Assam, India, and south-central Bhutan. The golden langur has experienced severe habitat loss and fragmentation due to ethnolinguistic and religious conflicts between the late 1980s and late 1990s, followed by developmental activities in western Assam. The primary threat faced by the golden langur in India are the rapid reduction of its natural environment and the fragmentation of its habitat. Factors such as a limited population size, the breakdown of meta-population dynamics, and unique traits of a species often make a population in a fragment more likely to experience local extinction. Due to the significant decline in the range of Golden langur in both Bhutan and India, as well as the ongoing destruction of their habitat in India, it is imperative to safeguard even the smallest local populations. The populations residing in these fragmented Reserved Forests and Proposed Reserved Forests are effectively confined, separated from the primary breeding population, and susceptible to demographic and genetic influences. The objective of this study is to understand the current distribution, suitable habitat, and connectivity of corridors for the severely fragmented southern population of golden langur in India. Additionally, the study aims to examine the specific habitat preferences and demographic patterns of langur groups, as well as evaluate the threats that this fragmented population faces. The study was carried out in nine fragmented forest patches that includes Wildlife Sanctuary (WLS), Community managed RF (CMRF) Reserved Forest (RFs), and Private Rubber Plantations and Adjoining Forests (PRP_AF). In the present study, a total of 123 trails, ranging from 0.4 km to 1.6 km, were walked, covering a total distance of 118.72 kilometers. During these surveys, a total 51 troops (including 8 multi-male multi-female troops and 5 all-male groups), consisting of 499 individuals were encountered. The mean group size and age-sex ratio between different protected regimes that include wildlife sanctuary (WLS), community managed RF (CMRF), reserved forest (RF) and private rubber plantation and adjoining forests (PRP_AF) were compared. The overall mean group size of the langur was 9.78 (± 0.69 SE). Of the total 499 individuals, 13.22 % comprised of adult males, 41.88 % adult females, 16.83 % sub-adults, 10.02 % was juveniles and 18.03 % was infant. The average age-sex ratio of adult males to adult females was 0.287 (± 0.04 SE), juveniles to adult females was 0.224 (± 0.02 SE) and infants to adult females was 0.407 (± 0.04 SE). The infant to female ratio was found higher in wildlife sanctuary as compared to other reserved forests in the study area. The current study revealed that approximately 883 km² of the area is highly suitable for the endangered golden langur. Percent forest cover was found to be the most important variable in determining the probability of occurrence of golden langur in India. The corridor connectivity analysis showed high conductance for corridors namely Bamungaon and Khoragaon RF. Similarly, the connectivity is permeable between Kakoijana and Bamungaon. Other corridors identified in the study are Bhumeshwar Hill, Nakati RF and Kakoijana RF. On the other hand, there is high conductance among corridors of Chakrashila WLS and Nadangiri RF. Additionally, fine scale habitat selection study showed that tree species diversity, canopy cover and food plant density are the key in determining the occurrence of golden langur. In the last six years, a total of 56 mortality and injury incidents were reported from the study area which include 45 deaths and 11 injuries. Electrocution accounted for 29 cases, especially near forest edges, while 21 road accidents occurred mainly on national and state highways, as these roads are broader and have higher traffic volumes compared to village and town roads. Most accidents happened in the corridors between Chakrashila WLS-Nadangiri RF and Kakoijona RF-Bamungaon RF. Specific measures need to be taken to minimize electrocutions and road accidents of golden langur in the region. Mitigation measures like insulating electric lines and road safety protocols such artificial canopy bridges (ACB) and metal animal overpasses (MAOP) are essential for safe and easy movement along these corridors for the golden langur's survival in fragmented habitats
Implementing artificial canopy bridges to connect fragmented population of Hoolock gibbon in Hollongapar Gibbon Sanctuary, Assam
(Wildlife Institute of India, Dehradun, 2023) Jha, R.R.S; Zangmo, S.; Gopi, G.V.
Habitat loss and habitat fragmentation are two principal threats to most terrestrial biodiversity across ecosystems and geographies. Gibbons are a particularly vulnerable group of primates inhabiting the forests of South and Southeast Asia. Of the 20 gibbon species – all threatened, according to the International Union for Conservation of Nature or IUCN – the endangered Western Hoolock gibbon Hoolock hoolock is the only one found in India inhabiting the forests in the southern bank of the Brahmaputra-Dibang river system. The Hollongapar Gibbon Sanctuary (HGS) is a small ~21 sq.km Protected Area (PA) in Jorhat, Assam and is one of the species’ stronghold supporting around 125 individuals living in more than two dozen family groups. It is also the only PA in India named after a primate species. Apart from the W. Hoolock gibbon, the Sanctuary also harbours six other primate species – capped langur Trachypithecus pileatus, stump-tailed macaque Macaca arctoides, northern pig-tailed macaque M. leonina, Assamese macaque M. assamensis, rhesus macaque M. mulatta, and Bengal slow loris Nycticebus bengalensis, thereby having the distinction of harbouring the highest primate species diversity for any Indian PA. However, a single track ~1.65 route-km long railway line (currently broad-gauge, but un-electrified as yet) has fragmented the Sanctuary since 1887 into two unequal parts. Over time, the Sanctuary has become a ‘forest island’ having lost connectivity with surrounding forest patches. Since gibbons are exclusively arboreal animals inhabiting the forest upper canopy, they are particularly sensitive to canopy gaps. Gibbon families on both sides of the railway track have, thus, been effectively isolated from each other, thereby compromising their population genetic variability and further endangering their already threatened survival in the HGS. Worldwide, and even in India, several conservation initiatives have attempted bridging such canopy gaps in forests through artificial canopy bridge (ACB) structures to facilitate arboreal species’ movements. The Wildlife Institute of India, Dehradun was approached by the Divisional Forest Officer, Jorhat (Territorial) Division of the Assam State Forest Department (ASFD) to provide specific design inputs towards the installation of such canopy bridges at the HGS. In this context, this report provides design guidelines and considerations as well as specific location-wise details of seven (07) potential sites within HGS for such canopy bridges installation, following thorough literature survey, field data collection and interaction with stakeholders such as ASFD officials and field staff, railway officials and consultants, and local conservationists. We recognise and emphasise that the design, successful installation and post-installation monitoring of canopy bridges require the involvement of several individuals with professional expertise in fields such as forestry, ecology/primatology, engineering and mountaineering/climbing. Post-installation monitoring of the canopy bridge structures – both behavioural observations of animals around canopy gaps and installed structures as well as through arboreal camera traps to assess bridges’ use – is one of the most important aspect of this project. As is clear, the present un-electrified single-track ~1.65 route-km railway line passing through the HGS has caused distress and posed significant conservation issues to arboreal animals. Hence, a future doubling of the line (if planned) will increase the canopy gap to a large extent and render any conservation interventions (such as ACB installations) futile. Over the longer period of time, it will be best if the status quo is maintained, although electrification of the existing single track may be permitted subject to necessary statutory approvals with appropriate mitigation and compensation measures implemented after detailed investigation of its ecological impacts. Forest regeneration on both sides of the existing track through afforestation activities to gradually enable natural canopy connectivity, adherence of trains to speed limits when passing through HGS and its Eco-Sensitive Zone/wildlife corridors, ensuring landscape connectivity of the isolated ‘forest island’ HGS with neighbouring patches of forests, and rerouting of the existing railway line outside Sanctuary limits, and establishing and supporting low-impact home-stay based ecotourism facilities are some of the longer-term interventions necessary to ensure that W. Hoolock gibbons and other canopy-dwelling species persist and thrive within HGS and in the immediate larger landscape.
Mitigation and monitoring measures for proposed high-level bridge construction through Son Gharial Sanctuary on Bahri-Hanumana road state highway-52 near Jogdah, Madhya Pradesh
(Wildlife Institute of India, Dehradun, 2022) Gopi, G.V.; Frank, S.J.D.; Arya, S.K.; Manisha, B.
The present study was conducted during the month of June and July, 2022. We performed transect walks (each of minimum 5 km) and sign survey on the east and west direction of the proposed Jogdah bridge along the north and south river banks of the Son River. The survey was conducted with the aim to assess the faunal diversity and its abundance and identification of important breeding and roosting sites of the birds and reptiles.
Nesting ecology of colonial waterbirds at Bhitarkanika mangroves, Orissa
(Wildlife Institute of India, Dehradun, 2010) Gopi, G.V.; Pandav, Bivash
Colonial nesting is an important feature among a majority of the members of Pelicaniformes and Ciconiiformes. The nesting colonies of these birds that represent spatial and temporal clumping of nests are popularly referred to as heronries. One of the largest heronries in India is located in the Bhitarkanika mangroves, along the east coast of India. Birds use five species of mangrove trees for nesting which include Excoecaria agallocha (Guan), Heritiera fomes (Bada Sundari), Cynometra iripa (Singada), Hibiscus tiliaceus (Bania), Tamarix troupii (Jagula) for nesting in the heronry. . The breeding birds in this mixed species colony are Asian Openbill, Great Egret, Intermediate Egret, Little Egret, Cattle Egret, Grey Heron, Purple Heron, Black-crowned Night Heron, Little Cormorant, Darter, and Black-headed Ibis. The heronry in Bhitarkanika is located in an island covered with mangrove vegetation. The availability of large number of nest trees in terms of the mangrove forest and foraging areas in terms of the wetlands inside the forest and the paddy fields surrounding the forest are believed to be the factors favouring such large congregation of breeding water birds in the heronry
Occupancy Pattern and Food-Niche Partitioning Among Sympatric Kingfishers in Bhitarkanika Mangroves, Orissa
(Wildlife Institute of India, Dehradun, 2011) Borah, Joli; Pandav, Bivash; Gopi, G.V.
Eight species of kingfishers, Common, Collared, White-throated, Pied, Stork-billed, Black-capped, Brown-winged and Rudy, - coexist in the mangrove forests of Bhitarkanika along the east coast of India. Sympatric species with similar resource requirements need to have niche partitioning as a strategy to avoid competition in order to coexist together. To understand the mechanisms underlying such species coexistence, it is vital to know about the food requirements, foraging habitat preference, and how the resources are shared between these sympatric species. The present study attempted to understand the potential mechanisms that might play a role in food-niche differentiation and examined the occupancy patterns of four sympatric kingfishers i.e. Common, Collared, Black-capped and Brown-winged kingfisher in Bhitarkanika mangroves. I conducted field study from January to May, 2011 in Bhitarkanika mangroves. The creeks were catgorized as primary, secondary and tertiary creeks based on the branching pattern. A total of 16, one km trails were selected in the intensive study area. Each 1 km trail was further divided into 10, 100 m segments for Sub-sampling. During the survey only seven among the 10 segments of each 1 km trail were surveyed which were selected randomly with replacement. A total of 160 creek segments of 100 m length were surveyed for six times during the study period and relevant habitat variables were recorded. For foraging behaviour observation, point count method was used i.e., an individual bird was followed till it captured a prey and relevant foraging variables were recorded. A total of 53 independent prey captures were recorded for the four species of kingfishers. Focal animal sampling method was used and observations were made opportunistically for time budget observation. Detection histories were constructed for each segment for bird survey and all relevant covariates. The two model parameters i.e., the probability that a segment is occupied by the species ('I') and the detection probability (P) were estimated and analysed in the occupancy framework. For foraging behaviour and time budget analysis, different parametric and nonparametric tests were used. Occupancy analysis confined that Collared and Black-capped Kingfisher occur seasonally in Bhitarkanika mangroves; Collared being more abundant in summer and Black-capped in winter. For all the four sympatric species river/creek width had a negative association with detection probability. Habitat type also affected the detection probability of all the species except Collared Kingfisher. The detection probability of Common and Black-capped Kingfisher decreased with the increase in depth whereas it did not affect the detection probability of Collared and Brown-winged Kingfishers. Water current and turbidity were negatively associated with the occupancy of Common and Brown-winged Kingfisher. However for Collared and Black-capped Kingfisher, it differed with vegetation layer. Perch height and foraging distance differed significantly among the four species of kingfishers. All the prey characteristics i.e., prey type, prey size and foraging substrate differed significantly among the four species of kingfishers. This study reveals that each of the four species of kingfishers in Bhitarkanika mangroves occupy foraging niches corresponding to their respective body sizes. The occupancy pattern and foraging behaviour of the smallest species, i.e., Common Kingfisher and the largest species, i.e., Brown-winged Kingfisher is more similar. As, both mostly forage in water to catch fish, their occupancy is also determined by water current. They segregate in terms of prey size, which is reflected by the respective body sizes. On the other hand, the foraging behaviour of Collared and Blackcapped Kingfisher is similar in terms of prey characteristics.
Patterns of Avian Diversity in different land-use and forest patch size of Kumaon Himalayas, Uttarakhand
(Wildlife Institute of India, Dehradun, 2021) Arya, Sumit Kumar; Gopi, G.V.
The present study was conducted in the Pithoragarh districts of the Kumaon Himalayas in Uttarakhand. The point count method was performed in matrices of agriculture land and forests of the lower Pithoragarh district to assess bird diversity patterns in different land use, habitat types, and disturbance regimes. A multiscale landscape heterogeneity approach was performed for determining the impact of forest patch size and vegetation structure on bird diversity. For assessment of the seasonal changes in the bird diversity pattern, a village ecosystem was monitored in the landscape.
Patterns of foraging in Olive Ridley Sea Turtle (Lepidochelys olivacea) Population on the East Coast of India and Habitat Characteristics of the Arribada Nesting Ground at Rushikulya
(Wildlife Institute of India, Dehradun, 2019) Mudliar, Mohit; Sivakumar, K.; Gopi, G.V.; Shankar, Karthik
This study was conducted and aimed to explore the patterns of spatial segregation of foraging olive ridley turtles which nest on two distinct nesting areas of the eastern coast of India; secondly, to examine the characteristics of mass nesting ground of Rushikulya; and lastly, to assess the status of microplastic presence in mass nesting ground. The study found that the moisture contents and sand particle size were homogenous across the beaches of Rushikulya. The sandbar had most extreme values for four of the five studied habitat characters which might be due to surrounding waters. Sea turtles those stranded during December to February at Chennai as well as Rushikulya seems to be from a similar type of foraging areas as their carbon isotope ratio were not different
Resource Use and Distribution of Smooth-Coated Otter (Lutrogale perspicillata) in the Sub-Himalayan Foothill Rivers of Uttarakhand
(Wildlife Institute of India, Dehradun, 2019) Basak, Sayanti; Hussain, S.A.; Gopi, G.V.
Otters are the apex predators of the wetland ecosystems they inhabit. Being sensitive to both pollution and habitat destruction, the presence of otters in a wetland ecosystem, be it rivers, lakes, swamps, mangroves or estuaries, indicates the occurrence of a viable prey base, thus indicating an ecologically healthy condition of such ecosystems. Coupled with habitat, prey is one of the major factors that limit species populations. Many species, including otters, are often seen to cope up with disturbed surroundings only for the easy accessibility or abundance of prey in those areas. The aim of this study was to understand the ecology of Smooth- coated Otter (Lutrogale perspicillata) in terms of their habitat requirements, food habits, and distribution across the landscape. The study was conducted in select rivers of Rajaji National Park and Tiger Reserve, Lansdowne Forest Division, and Corbett National Park and Tiger Reserve. These protected areas fall in sub-Himalayan region, a region of high biodiversity value threatened by immense anthropogenic pressure. Habitat parameters were measured at every 250 m along a river bank and also in locations where there were otter evidences. The importance of different habitat parameters influencing otter occurrence were analysed using Generalised Linear Models (GLMs) and non-mapping technique using Bonferroni confidence interval approach. Smooth-coated Otter significantly preferred deep pools with moderate to sparse bank-side vegetation during the mid-winter and late-winter season. Moderate width water bodies are preferred over narrow water bodies. Muddy and sandy bank substrate types were preferred. Rocky stretches were largely avoided. Water body type i.e. pools and bank substrate type, i.e. rocky substrate, are the significantly influencing factors on otter distribution. Feeding habit of otters were studied by analysing 120 spraints collected throughout the study area. In this study, we also explored how the habitat suitability modelling could predict the percentage of area and a gradient of environmental conditions suitable for the occurrence of Smooth-coated Otter across the study area. MaxEnt modelling was used to predict habitat suitability of Smooth-coated Otter across the landscape. The most important variables affecting otter distribution were compound topographic index, Euclidean distance from the river, and slope position index. With increasing distance from water, and increasing slope, the suitability of an area to sustain otter populations decreased.