M Sc Dissertation(WII)
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Item Factors Governing the Spatial Distribution and Density of Asiatic Lions (Panthera leo persica) in Gir Protected Area(Wildlife Institute of India, Dehradun, 2015) Gogoi, Keshab; Jhala, Y.V.; Qureshi, QamarThis study is based on population estimation and spatial distribution of Asiatic lion.Item Assessing Population Status Roost Site Selection and Fruit Damage by the India Fly fox Pteropus giganteurs in Southern Karnataka: The Flying Foreesters(Wildlife Institute of India, Dehradun, 2015) Raj, Versha M.; Qureshi, QamarFlying foxes Pteropus giganteus, playa key role in pollination and forest regeneration as seed dispersers. Despite this beneficial role, they are persecuted for being an agricultural pest in commercial orchards. More recently in India, they have been known to be reservoirs of deadly zoonotic diseases like Nipah. Over the past two decades rapid urbanization, leading to habitat and roost tree destruction has resulted in decline in population of the Indian flying fox. As a result, incidence of flying foxes visiting commercial orchards has increased which in tum has led to conflict between large-scale commercial fruit growers and flying foxes. Assessing the present population status, and identifying the habitat preferences could help in understanding the risk of fruit damage in the surrounding areas, and will help in conservation of the keystone species and there by prevent their persecution also. A total of 51 roosts were identified which were used to assess the population status and change over time. Four methods of population estimation were compared to select the most reliable. method. Photographic count method was found to be most reliable for of population estimation. At the landscape level, proximity to water bodies and intensity of urbanization influenced the occurrence of roosts. 11.38 % of the total study are was found to be suitable for roosting (potential habitat). Amongst the individual tree characters, tree GBH and tree height were found to strongly influence the roost selection. In commercial orchards, Pteropus giganteus was found to be responsible for significant amount of damage in orchards cultivating Guava, Mango and Sapota. Based on the extent of damage they were ranked second most important animal pest in these commercial orchards after birds. Further work on estimating actual fruit damages would be required to confirm the role of the Indian flying fox as pest responsible for causing severe fruit damages in commercial orchards, for which they have been constantly persecuted.Item A Whistle Amongst Growls : Dholes in a Multi Predator System in Dry Deciduous Forests of India(Wildlife Institute of India, Dehradun, 2015) Ghaskadbi, Pallavi; Habib, Bilal; Qureshi, QamarA significant amount of research has proved that there is a positive correlation between habitat heterogeneity/diversity and animal 'species diversity owing to the availability of more exploitable niches (Tews et al. 2004). On a spatial scale for free ranging large carnivores, a place like the Tadoba- Andhari Tiger Reserve has a low habitat heterogeneity, however, it shows a variety of species of both predators and prey in a small area. Studying the prey- predator interactions in such a system would lead to a better insight into large carnivore ecology. In contrast with the African Wild dog which enjoys much more attention of researchers and biologists, the Dhole has clearly not been a favourite. Being a social carnivore, there is a complex and dynamic fission and fusion of packs amongst Dholes. However, there is a grave lack of information on the pack dynamics of the Dhole. I attempted to conduct experiments to study one of the fundamental factors of social behaviour which is individual recognition.Item Study on the Trends of Bushmeat Consumption and Traditional Hunting on Wild Fauna by Indigenous Community Living Near Protected Area in Nagaland.(Wildlife Institute of India, Dehradun, 2013) Longchar, Satemmenla; Qureshi, Qamar; Jhala, Y.V.Bush- meat Hunting is an integral part of a man's life specially people living in an indigenous community. This practice has evolved since primeval time. This has been rooted in the culture and traditions which plays an influential role in keeping those practices alive. Hunting is an art. And these arts are an integral part of shaping a man's role in the society. This is however becoming a calamitous action in destroying wildlife, often driving them into extinction-at global and local scale. With the over growing populations in the world and a huge demands for wildlife globally, for consumption, medicinal values, for clothing, and traditional adornments, these factors eventually lead to extermination of species at a rapid speed. Nagaland is in a region recognized as a biodiversity hotspot, in spite of the rampant hunting activities across the state. My study site Intanki National Park is located in Peren District of Nagaland. This park is categorized as Northern subtropical broad leave forest type. This park adjoins neighboring state of Assam's Dhansari reserve forest and hence an important area for connectivity for species. I conducted my field study from December 2012 to April 2013 in Intanki National park, Nagaland. I choose 6 sites for my study based on hunting intensity. A total of 60 transects of 1 km each was walked on the human and animal trails for estimating abundance of both mammal and birds separately. Along with that 240 plots for tracks and pellet count were sampled to estimate relative mammal abundance index. Camera traps sampling at each of the 6 sites vary from 50-99 trap nights. Relative density estimation of mammals from pellet results highest in site Camp2 with1.75 (0.34) and least in the community reserve with 0.22 (0.09), whereas relative density estimation for track plot was highest in site Longkhor Disa (1.4 (0.22) and least in community reserve (0.37 (0.02). For mammals the density estimation was 25.02 (3.64),for the bird's density, the highest was found in small sized birds with cluster size of 114.38 per sq.km, lowest density was for ground dwelling birds at 13.68 birds per sq.km. Site Occupancy (\f') and species richness for birds and mammals from camera traps and transect (n=60) was estimated at six sites. Data indicates that species richness of birds is highest in camp 2 (38) and least in Hatibu Disa (25). Richness of mammals was higher in the community reserve (20) and least in Hazab Disa area (5). The capture rate of all the species was higher in junction camp where as the lowest photographic capture rate was obtained from Hazab Disa. I surveyed a total number of 94 households and 16 hunters across 6 villages. From the questionnaires it was found that the Indian muntjac, common palm civet, jungle fowl and wild , pig are the most preferred species with 100% positive response from 94 households surveyed, for consumption. Traditional hunting techniques are being replaced by the modem Guns for killing animals. Besides, demand of wild animal for traditional medicinal usage also contributes to the hunting of animals. It was observed that hunting does not impact species richness. However, in mammals, there is negatively impact on ungulates (pellet density and encounter rate). For birds, the significant negative effect is found only on the medium sized birds. Equilibrium density (density to support hunting) was calculated by Individual hunted per year per 100 sq.km / growth rate. In my study, the deficit of species due to hunting was found most effective on Indian muntjac and Common palm civet. Over harvesting of this species through hunting will result in decline of the species population. I estimated sustainability of hunting and found out that most of the species are hunted beyond sustenance level; hence, if this is continuous, it might result · in the population and local extinction. In conclusion, in a society where bushmeat is an essential source of proteins, it is important to realize the current status of wild fauna and hence emphasis should be given to control and promote alternative.Item Evaluation of Population Estimation Sampling Techniques and Assessment of Genetic Diversity of Greater One-Horned Rhinoceros (Rhinoceros unicornis) Population in Dudhwa National Pa: Population in dudhwa national park, uttar pradesh, India(Wildlife Institute of India, Dehradun, 2013) Srivastava, Vibhav; Goyal, S.P.; Qureshi, QamarThe ideology of wildlife conservation emerged with the realization that the wildlife numbers are on a decline in the natural habitats. Since, due to humane limitations we cannot ascertain the exact numbers of a individuals very accurately, therefore, the basic requirement for population estimation arises. Greater one-horned rhinoceros (Rhinoceros unicornis) , already being declared a globally threatened species, demands much attention towards their surviving numbers in wild. Moreover, with the constant rise in the unethical and illegal human activities, the need to regularly monitor their population is realized. To suffice this requirement, population estimation is largely done in a crude way i.e. by labor intensive block count method in which the probability of missing individuals in dense vegetation is high. Advanced population estimation techniques such as capture-recapture using photographic or DNA fingerprint based individual identification, show promising results within the framework of resources in comparison to use of footprint and dung count methods.The current study was conducted in Rhino Reintroduction Area (RRA) of 27 km2 located in Dudhwa National Park. The first objective was to evaluate four population estimation techniques - non-invasive faecal DNA based capture mark recapture (CMR), photographic CMR, dung count and footprint analysis, for their validity in estimation of rhinoceros population with respect to accuracy and precision. The following techniques have been selected out of the others because of their reasonable accuracy and precision obtained when applied to other megaherbivore (including other species of rhinoceros or elephant) population estimation. I selected Dudhwa National Park (DNP) where the reintroduced rhinoceros population is surviving since 1984-85, with a known population size (32 individuals) so as to compare our estimates. For non-invasive faecal DNA CMR technique 140 fresh dung samples were collected and out of them 27 unique genotypes were identified by microsatellite analysis. The capture history of these unique genotypes was then analyzed in MARK to arrive at a population estimate. In photographic CMR, 4 remotely triggered camera trap units were deployed in 6 sessions having 7 occasions in each session. For dung count, random elephant transects of length varying from 1 km to 3.2 km were run and dung piles were counted on either sides. The data on dung density was analyzed in DISTANCE. For dung decay rate estimation 20 fresh dung piles were marked in each of the four habitat types and monitored for decay. The defecation rate was estimated by observing captive rhinoceros. In case of footprint technique, a foot ruler was kept besides each rhinoceros footprint before capturing its photograph. Twenty four (length, angle and area) parameters were extracted from the images using Sigma SCANPRO. The resulting variables were subjected to principle component analysis (PCA) to check for the corresponding variance values in differentiating individual footprints. It was found that the· non-invasive faecal DNA based population estimation and photographic capture mark recapture were the better ones as compared to the other two. However, the data analysis for the dung count and footprint analysis techniques is still under consideration and does not form part of this thesis. These two techniques require further logical modification in study design and statistical analysis to achieve at a reliable estimate. Between the former two, non-invasive faecal DNA based population estimation technique estimated population size (35.10 ± 5.01) close to the known population size of 32. Photographic capture recapture estimated the population size as (25.98 ± 4.91) which was comparatively less accurate than non-invasive faecal DNA CMR. Knowledge of the genetic status of a confined and isolated population is always beneficial to evaluate their well-being and to avoid any future threat such as that of inbreeding depression. Therefore, second objective of the study> was to describe genetic structure of this isolated and reintroduced population. With 27 identified unique genotypes and 10 rhinoceros specific micro satellite markers the genetic variability in this population was examined. It was found that the mean observed heterozygosity level was 0.353 while mean expected heterozygosity level was 0.483. The effective number of alleles per loci was 2.069. When compared to the genetic diversity of the ancestral population in India and Nepal, evaluated in previously published studies, the following results indicated that this population carries lower genetic variability than ancestral populations. The inbreeding test revealed that the population shows signs of inbreeding (Fls = 0.39) and which are likely to exaggerate in future as it is more or less closed and non-randomly interbreeding. Focusing on the conservation needs from management viewpoint we suggest that it is necessary to 'bring variability in the genetic structure to avoid future dire consequences of inbreeding depression. This can be achieved either by translocating new individuals, preferably males, from other Indian sub-populations of Assam or West Bengal since they have better genetic diversity than the-rhinoceros in Nepal.Item Computing Biomass Consumption from Prey Occurrences in Scats of Tropical Felids(Wildlife Institute of India, Dehradun, 2013) Chakrabarti, Stotra; Jhala, Y.V.; Qureshi, QamarA robust understanding of prey use and selection by carnivores provides crucial insights into their ecology, conservation and management. In majority of the cases, scat analysis is most effective to assess diet spectrum of carnivores, but require correction for potential biases for estimating biomass contribution of different prey items. Since small prey have higher indigestible matter per unit body mas~ due to higher surface area-to-volume ratio, relative frequencies of prey remains in scats do not represent their consumed biomasses. Thus ~ to accurately estimate the proportions of different prey consumed, it is necessary to develop relationships between biomass consumed per field collectable scat and prey weight through feeding experiments. However, no such relationship exists for felids of the Indian sub-continent. The studies on diet of big cats like lion (Panthera leo), tiger (Panthera tigris) and leopard (Panthera pardus) have used a similar relationship based on cougars (Puma concolor) by Ackerman et al. 1984 owing to the unavailability of any species specific relations. Methods: A series of feeding trials were used on Asiatic lion (Panthera leo persica), leopard and jungle cat (Felis chaus) to develop prey incidence to biomass conversion equations (hereafter mentioned as biomass models or biomass equations). Principal findings: All the models showed satiating relationships between biomass consumed per collectable scat and prey weight given by asymptotic exponential functions. However, carnivore specific models when scaled to their respective body weights did not differ significantly between each other, allowing derivation of a generalized biomass model for tropical felids. Inferences using present study models refined existing representation of diet of tropical carnivores. Significance: Results from the present study have strong implications on feeding ecology of tropical felids. Present study refined previous understanding of biomass contribution of different prey species in large felid diet by substantially increasing roportion of medium prey consumption. Such inferences question niche separation of sympatric large felids on the basis of prey species of different sizes, where large carnivores like tiger optimizing on large prey like gaur (Bos gaurus) and sambar (Rusa unicolor). while medium felids like leopard maximizing on chital (Axis axis). Domestic livestock significantly reduced in carnivore diet, reducing livestock depredation rates. indicating lower human-carnivore conflict levels.Item Abundance, Habitat Relationships and Behavior of the Semi-Fossorial Indian Desert Jird, Meriones hurriancae, in Kachchh, Gujarat(Wildlife Institute of India, Dehradun, 2011) Ramesh, Divya; Jhala, Y.V.; Qureshi, QamarPopulation sizes, habitat relationships and behaviour are among basic ecological aspects pivotal to demystifying a species and its place in the ecosystem. Numerous in species and number, desert rodents offer immense scope for such investigations. The Indian desert jird, Meriones hurrianae, though common, is remarkably little known. This study, conducted in Kachchh, Gujarat, estimates population sizes, examines factors in the habitat likely to influence their occurrence, and elucidates the activity pattern and time budget across 2 land use types, agricultural and natural areas, during winter (December February) and summer (March-May). Animals were caught in 9 colonies using Sherman traps and population estimated under closed population Capture-Mark-Recapture framework in Program MARK, using individual covariates (age class, gender, body weight, site). Colony parameters (length, width, number of holes) were regressed against known Mark-Recapture (MR) population estimates to develop predictive models for estimating population size from indices. Population sizes varied from 2 to 10 individuals. Number of holes in a colony provided robust estimates of the number of individuals in that colony (N=16, R2=0.96, t=18.19, pItem Responses Shown by Bird Communities to Teak Palatations in Sagar Forest Division, Karnataka(Wildlife Institute of India, Dehradun, 2009) Barve, Sahas S.; Mohan, D.; Qureshi, QamarThis study was aimed at discerning the responses shown by bird communities to teak plantations of various age classes in Sagar Forest Division, Karnataka within Latitude 13° 36' and 14° 38' North 74° Longitude 38' and 75° 32'East Latitude. Birds were sampled using line transects in three habitat strata, natural plantations, mature teak plantations and young teak plantations. Density, diversity and community similarity were the chief ecological responses that were quantified to bring out differences in the usage of forest plantations by native bird fauna. Habitat (vegetation) correlates, both structural and floristic were quantified to establish the reasons for differences. The sampling period was from December 2008 to April 2009. This period was divided into two seasons, winter and summer. A total of 9 transects were laid, marked and sampled at least 4 times per season. Birds were divided into three feeding guilds and three habitat guilds for analysis. The overall density of birds across the three strata was found to be higher in summer than in winter. However a guild level analysis showed that in winter while insectivorous birds were most abundant in natural forest with decreasing density towards young plantations (F (6.241) , p< 0.05). There was no difference in their density in summer. Phytophagous birds showed the exact reverse trend. Density of this guild was higher in young plantations than natural forests and mature plantations in winter and summer (F(S.689), p< 0.05), (F (14.302), p< 0.01) respectively. Overall diversity of birds showed a trend of decreasing species richness from natural forests to young plantations in both seasons. However this difference was almost non existent in summer at the guild level. The abundance of birds belonging to evergreen and moist deciduous forests shows a consistent· rise in abundance from winter to summer in all the three strata. There is also evidence that there is ingression of individuals of species that were common to both seasons possibly for nesting. The overall community similarity is quite high between the three strata and it increases from winter to summer. Bird diversity was found to be affected by the vertical spread of vegetation and tree height heterogeneity (R=0.871, pItem Interaction of Kiang (Equus kiang) with Livestok in Hanley Valley of Chanthang Wildlife Sanctuary, Ladakh(Wildlife Institute of India, Dehradun, 2009) Hussain, Asif; Qureshi, Qamar; Rawat, G.S.Hanley Valley «320 41' 27" N 790 04' 3.5") in Eastern Ladakh forms the western most extension of Tibetan plateau and has been recognized as an important biogeographic province in India (Indian Trans-Himalaya). This region harbors a rich array of wild and domestic ungulates. The area is also home to nomadic Changpa and Tibetan refugee herders. The political, social and ecological transformations have altered previous, well-established links between the pastoral population and their rangeland environment. Over the years, with growing integration of the local economy of Ladakh and with better development of cash markets, the pastoral community is fast losing its tolerance towards the kiang and it is increasingly seen as a competitor to livestock. The purpose of this study was to document this intensifying conflict between pastoralism and Kiang conservation, using resource selection functions. Data on habitat variables were collected on 4 fixed trails of varying length (3- 7 km) for kiang (with and without livestock presence) and livestock for use availability analysis. For food habits, micro-histological method in case of kiang and bite count method in case of livestock was used. Data on activity pattern of kiang was collected to examine change in response to livestock presence. Density and encounter rates were estimated using vehicle transects (n=5) of varying lengths (5-56 km). Livestock were followed (focal animal sampling) from dawn to dusk to estimate amount of forage removed. Availability of different habitat variables was estimated using ArcGIS 9.2. Total of 104 kiang groups before arrival of livestock and 187 kiang groups after livestock arrival to the area were recorded. Habitat use by kiang and livestock was significantly different (8 = 0.00016, P < 0.05). Habitat use by kiang before and after livestock arrival was found to be significantly different (8 = 0.013, P <0.05). Groups of kiang were observed (n=14) for time budget evaluation, 7 prior (640 min) and 7 (820 min) after livestock had come to the area. Activity pattern of kiang before and after livestock arrival was found to be significantly different (8 = 0.04, P <0.05). Food preference for kiang before and after livestock arrival was not found to be significantly different. Food preference for kiang and livestock was significantly different (6= 0.0000007, P < 0.05). Use-availability analysis suggested differential selection for food plants. Schoener's niche overlap for food items found moderate overlap between kiang, sheep and goat «60%) and high overlap between kiang and horse (>80%). Forage removed (kg) by sheep, goat and horse were 2.33 kg, 2.25 and 8.19 kg respectively. Total density and encounter rate for Hanley valley was 0.07 kiang/km2 and 0.45 kiang per km respectively. The difference in habitat use translated into Kiang using higher elevations while livestock used middle elevations more than available. Kiang used steep slopes whereas livestock used steep as well as gentle slopes more than available. Kiang used North-West aspect more than available. Kiang used vegetation communities dominated by graminoides while sheep-goat used communities dominated by shrub and forbs. Density and encounter estimates did not show considerable increase in kiang population compared to previous studies. Hence, the perception of people of kiang overstocking in the study area appears to be misplaced. Detailed perception studies should be carried out in the whole of Changthang and herder-centered participatory programmes need to be carried out on a large scale to ensure long term conservation of kiang in eastern Ladakh.Item Estimating the Status and Impact of Hunting on Tiger Prey in Bardia National Park, Nepal(Wildlife Institute of India, Dehradun, 2009) Malla, Sabita; Jhala, Y.V.; Qureshi, QamarA study was undertaken to understand the status of tiger prey species in relation to the hunting pressure in Bardia from November 2008 to April 2009. The prey densities were estimated using distance sampling