Theses and Dissertations
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Item Characterization of bone, ivory, Rhino horn and antler to deal wildlife offence cases.(Wildlife Institute of India, Dehradun, 2007) Singh, Rina Rani; Goyal, S.P.Species for this study were selected according to the endangered status of the species and since these products were difficult to identify mostly in processed form. Therefore, attempts were made to characterize bones of tiger (Panthera tigris) and leopard (Panthera pardus), greater one horned rhinoceros (rhinoceros unicornis) horn and antlers of chital (Axis axis), sambar (Cervus unicolor), swamp deer (Cervus duvauceli). Other than these species mentioned in synopsis, antlers of hog deer (Axis porcinus) and barking deer (Muntiacus muntajak) and ivory of Asian elephant (Elephas maximus) have also been characterized for comparison purposes. The present study is an effort to develop methods to characterize these items for conservation of the concern species and objectives of this study are as follows: 1. Determine morphological, crystallographic (XRD & XRF) and DNA characteristics of major bones of tiger and leopard, and 2. Determine morphological, crystallographic (XRD & XRF) and DNA characteristics of rhino horn and antler of chital, sambar and swamp deer species.Item Factors affecting habitat occupancy of tiger in the Terai Arc landscape, India(Wildlife Institute of India, Dehradun, 2009) Rajapandian, K.; Goyal, S.P.; Qureshi, QamarThe goal of this study, therefore, was to identify the factors affecting the distribution of tiger and assess the distribution of suitable habitat patches and the connectivity between these patches for successful dispersal in the Indian part of TAL. In the present study developed GIS probability models for tiger and its prey species and a spatially explicit individual-based dispersal model (SEIBM) for tiger in order to identify and assess the factors which are affecting the occupancy of tiger and subsequently predict potential suitable habitats and estimate the connectivity between the fragmented subpopulations in the Indian as well as between Indian and Nepal part of TAL. Data were collected on presence/absence of four wild ungulates (sambar Cervus unicolor, chital Axis axis, nilgai Boselaphus tragocamelus, and wild pig Sus scrofa), which are important prey species of tiger in two phases during the period between 2002 and 2006. The results of this study, in addition to contributing to the knowledge on factors affecting suitable habitat distribution and dispersal of tiger, have many implications for conservation of tiger in the Indian part of TAL. This study has also identified critical areas needed for management initiatives for functional unit of tiger conservation in the TAL.Item Status and ecology of leopard (Panthera pardus) in relation to prey abundance, land use patterns and conflict with human in Garhwal Himalaya.(Wildlife Institute of India, Dehradun, 2007) Chauhan, Devendra S.; Goyal, S.P.The problem of human-leopard conflict has recently been increased in the Indian Himalayan region due to change in land-use patterns. Leopard-human conflict as predation on human and livestock has been quite frequent in 16 districts of Uttarakhand state and Pauri Garhwal district is worst affected. Recent increase in such incidences has been reported from this region. The main goal of this research was to provide a base line information on status of leopard-human conflicts in Pauri Garhwal district and response of leopard in relation to prey abundance, land use patterns and human dimension in human dominated landscape. Present study was undertaken in Pauri Garhwal district of Uttarakhand to (i) determine distribution and current status of leopard in Pauri Garhwal (ii) to determine extent and severity of leopard-human conflict problems in relation to its ecological requirements, land use patterns and human life style. (iii) to study food habits in relation to prey abundance (wild and domestic) and habitat characteristics and (iv) to determine factor responsible for leopard-man conflict. A survey was carried from February 2000 to October 2001 in 15 administrative blocks of Pauri Garhwal district. Information was collected on distribution and extent and severity of leopard-human conflict.Item Nutritional Ecology of Asian Elephants (Elephas maximus) in Chilla Range of Rajaji National Park, Uttarakhand(Wildlife Institute of India, Dehradun, 2009) Datta, Suniti Bhushan; Goyal, S.P.; Sathyakumar, S.Responses of animals to the habitat has been the central focus for management of species and of these aspects, nutritional ecology has been the key issue in foraging behaviour studies and habitat studies. Therefore, the study focused on the nutritional aspect of forage selection by Asian elephants (Elephas maximus) in Chilla Range of Rajaji National Park. The main objectives were to determine whether habitat structural heterogeneity or nutritional quality of the selected food plant species was a determinant in the temporal and spatial habitat use by elephants and to determine the reasons behind seasonality in foraging. The study area of 148km2 in Chilla Range of Rajaji National Park was divided into twelve 2x2km grids, and these were further divided into 4 sub-grids each. In each sub-grid, a 1 km long line transect was laid and along this 10m radial plots were placed at 100m intervals. Vegetation data were collected to characterize the habitat structural heterogeneity in terms of number of trees of each species, height of canopy base, canopy volume, percent canopy cover, species diversity, species density and geo-spatial variables such as NDVI, standard deviation of slope, mean elevation and the proximity to water. Parts of 12 most-preferred plant species were collected in the study areas for estimating nitrogen, ash, acid detergent fibre, and macro and micro minerals such as sodium, potassium, calcium, copper, magnesium and zinc. During the study period from December 2008 to May 2009, Elephant response was determined in terms of dung density along the 1km transect in winter and in summer. The total number of trees in each grid varied from 124 to 268. Tree diversity ravged betweel) 0.456-1.454. Height of canopy base was mostly 1.5-3.0 m, although two grids showed extremely high canopy bases. Canopy volume ranged from 165.63m3 to 948.36m3 , although the majority of the grids showed a high variation in canopy volume in terms of standard deviation (SE). The percent canopy cover ranged from 54.13% to 93.72%. Most of the NDVI values were _high in the study area (>0.180), while one grid showed a low value of 0.143. For the standard deviation of slope, the values ranged from a low of 2.46 to a high of 8.46. The mean elevation of the study area ranged froin 391-840m a.s.l. Nutritional values estimated for most of the parameters in winter and summer from selected plant samples collected in the study area showed slight variations 4 between seasons. Percent nitrogen content indicated no seasonal difference (f=0.98, p=0.05, df=ll). The percent acid detergent fibre indicated a difference (P<0.05,df=I I) between the two seasons. Percent ash content was found not significantly different (p=O.l6, p=0.05, df=l1) between seasons. Amongst the macro and micro minerals, sodium content was significantly different across the two seasons. Potassium content was found to be significantly different across the seasons (p<0.05). Calcium content was also found to be significantly different between winter and summer (P<0.05). The copper content could not be compared across the seasons as in summer the levels present in plant samples were too low to be detected by the instrument. The difference in magnesium and zinc content across the two seasons were not significant (p=0.16 and P=0.31). Dung density in the grids across both seasons was non-uniform and highly skewed (p<0.05, df=47). The dung densities in both seasons were related more with the habitat heterogeneity variables than nutritional values obtained in each grid. The relationship between dung density and the number of plants was positive in the winter seasons (R2= 0.2848) and summer (R2= 0.4383), indicating that elephants are highly selective towards areas with higher numbers of woody plants. Plant species diversity indicated no influence on dung density in winter (R2= 0.00005), but showed a negative trend in summer (R2= 0.0154). The height of canopy base was negatively related to dung density, with elephants selecting areas with a mean canopy base height between 1.5-3.0m during both winter (R2=0.2288) and summer (R2=0.174). Dung density showed a negative trend when related to canopy volume in both seasons. The R2 value for winter is 0.2087 and in summer it is 0.1471. Percent canopy cover had a negative influence on the dung densities in winter (R~= 0.083) and in summer (R2= 0.1524). NDVI showed a negative relationship with dung densities in winter (R2=0.01l1) and a positive relationship in summer (R2= 0.1894). The relationship between the standard deviation of slope and dung density showed a negative trend in both winter, (R2=0.0033) as well as in summer (R2=0.0389). The higher elevation grids show a lower d/mg density during both winter (R2=0.216) and summer (R2=O.l443). The relationship between dung density and proximity to water in winter is negative (R2=0.1575) and the relationship remains negative (R2=0.1016) in summer. In relation to nitrogen content and dung density in winter there was a weak positive trend (R2=0.0256), while in summer there was a weak negative trend (R2=0.032). The relationship between dung densities and percent acid detergent fibre (ADF) in winter indicated a weak positive trend (R2=0.0012) and during summer, indicated a weak negative trend (R2=0.0657). In relation to percentage ash content (Fig. 4.29.), dung densities in winter indicated a weak positive trend" (R2=0.0114), while in summer there was a weak negative trend (R2=0.0641). When compared with sodium, dung densities showed a very weak positive trend (R2=0.0092) in winter and a negative trend in summer (R2=0.0834). In winter, when compared with dung densities potassium showed no trend (R2=0.001), but in summer, there was a weak negative trend (R2=0.0076). In winter, calcium does not show any relationship with dung densities (R2=0.0002), while in summer, there is a weak negative trend (R2= 0.0511). Magnesium content does not show any relationship with dung densities (Fig 4.33) in the winter season, (R2=0.0007), while in summer, there is a weak negative trend (R2=0.004). Zinc shows a weak positive trend (R2=0.0298) in winter and a weak negative trend (R2=0.026) in summer. Principal component analysis of nutritional parameters indicated nine components that were influencing dung density distribution in the study area in both the seasons, and hence no single parameter influenced elephant habitat use. The study clearly indicates that the distribution of elephants in Chilla Range of Rajaji National Park is more related to abundance of woody species and proximity of water, than the nutritional content in plant species. Principal component analysis showed that there was no single parameter that influenced dung distribution in the study area. This could be due to the fact that plant species selected for foraging by elephants contained an adequate amount of nutrients in most species for meeting foraging requirements .an d they probably meet their daily requirements by foraging on varied proportions of plant species.Item Habitat Relationships and Resource Partitioning in a Lizard Community of the Thar Desert(Wildlife Institute of India, Dehradun, 2007) Agarwal, Ishan; Goyal, S.P.; Qureshi, QamarA lizard community in the Thar desert was studied in relation to habitat relationship resource partitioning and community niche pattern. The study was carried out in parts of Desert National Park, Jaisalmer district, Rajasthan, Four habitat types were recognized, barren dunes, stabilized dunes, grassland and rocky hills. A visual encounter survey was used to sample lizards within grids. Logistic regression was used to identify determinants of species presenceItem Assessment of Human-Elephant Conflicts in Jalpaiguri District of West Bengal in Relation to Land-Use Patterns(Wildlife Institute of India, Dehradun, 2003) Roy, Anirban Datta; Goyal, S.P.; Sathyakumar, S.This study on Human Elephant Conflict was conducted in Jalpaiguri district .of north West Bengal to identify the level of conflicts in different areas of the district, and to recognize it in connection with land-use patterns existing in the district. The study was conducted over five months and information on conflicts was collected from Tea Gardens and Wildlife Squads. Interviews and questionnaires were also used to survey the conflict affected viilages. The different conflict areas and the intensity of the conflicts in those areas were identified with the help of gridded maps. Results showed that although most of the conflict areas had remained the same from previous studies, some new conflict areas were also emerging. Seasonality of the conflicts was also found to be related to cropping patterns adopted. Information collected from the Tea gardens showed that the Tea gardens which had previously been categorized as high conflict areas had remained same to a great extent. The Tea gardens having the highest conflict incidences were frequented more by solitary animals rather than herds. The mean group size of the herds were found to show two distinct peaks in the months of May-June and September-November. Interviews with affected villagers provided a true picture of the difficulties faced by them during crop-raiding. In the absence of Wildlife Squads, villagers had to drive the elephants away with their own methods.Item Space Use Patterns of the Indian Giant Squirrel (Ratufa indica centralis Erxleben) in Relation to Food Availability in Bori Wildlife Sanctuary, M.P. India(Wildlife Institute of India, Dehradun, 1993) Datta, Aparajita; Goyal, S.P.The spatio-temporal heterogeneity of food supply and the consequent effects on food resource use and space-use patterns of the Indian giant squirrel (Ratufa indica centralis) in Bori Wildlife Sanctuary, was the focus of study. Territoriality, which may affect space-use patterns of individuals was of special interest. Climatic factors which may influence activity budgets and consequently the variability in seasonal space-use patterns are also discussed. Based on individual variation in physical characteristics, Z identified three focal animals (one male, one female and a subadult male) in the disturbed habitat (Bhainsa nala ) , and a male and female in the undisturbed habitat (Churnagundi nala) for whom dana could only be gathered in winter. Therefore seasonal changes in space-use patterns is discussed for focal squirrels in the disturbed habitat. I kept a continuous record of behaviours during focal animal sampling. Home areas were calculated based on hourly locations taken from focal data. I gridded the area used by focal squirrels and recorded the vegetation parameters. The seasonal change in resource availability was monitored by phonological observations on all trees in the grids twice a month. Squirrels in Bhainsa nala selectively utilised certain individuals of flowering and fruiting crees which was related to crop size. Squirrels included bark and leaves in their diet even when fruit resources were available. The resource use by squirrels in Churnagundi nala showed a marked difference from squirrels in Bhainsa nala in winter which was due to the poor availability of food. Individual squirrels in Bhainsa nala showed variation in food species, food items used and the percent time spent feeding on each food item indicating that resource availability was not the same for all squirrels. No significant correlation was found between resource abundance and percent use of the item. Squirrels had overlapping ranges but were otherwise solitary. Many preferred resources were rare in the habitat, and the spatio-temporal heterogeneity in food resources resulted in overlap between individuals at locally abundant food resources. Because of this heterogeneity, the defence of an exclusive area guaranteed of resources throughout the seasons is not possible. Therefore squirrel ranges overlapped, but encounters were avoided by spatial time sharing but when encounters occurred, overt aggression was seen. But at certain locally abundant resources which were located at the periphery of the home areas, squirrels tolerated each other by maintaining inter-individual distances (5-10m). The tolerance of conspecifics at these resources could also be related to the existence of dominance hierarchies which result in decreased over aggression. The intensity of use (time spent) decreased as the distance from nest increased for all squirrels. Squirrels made forays in search of food and in many cases foraging was in the peripheral areas of the range. The male’s range showed overlap with the female’s in winter which could be related to sexual activity. Squirrels had a bimodal activity pattern in both seasons but bimodality was less pronounced in the winter since activity was distributed throughout the day when temperatures were more equable Shift in onset and cessation of activity was observed with changing daylength. Time spent feeding in April was much less than in other months. Time budgets showed that in all months a higher proportion of time is spent resting which could be due to heat or cold stress in or time needed to digest food items eaten. in Activity pattern of the squirrels in winter in Churnagundir nala were influenced by the low resource availability which resulted in long basking and resting periods and negligible time spent in feeding. Though occasional forays of short duration were made, no food was located by these forays. Thus squirrels adopted a strategy of conserving energy by minimizing their requirements by resting.Item Habitat Use, Group Size and Activity Pattern of Goral (Nemorhaedus goral) in Simbalbara Sanctury (Himachal Pradesh) and Darpur Reserved Forest (Haryana) India(Wildlife Institute of India, Dehradun, 1993) Pendharkar, Anand; Goyal, S.P.A study on the habitat use, group size and activity patterns of goral (Nemorhaedus goral) was undertaken from November 1922 to May 1993 in Simbalbara Sanctuary (Himachal Pradesh) and Darpur Reserved Forest (Haryana). Data on availability of habitat types, vegetation types, slope, aspect and cover and their corresponding use (N=230 sightings), were collected along six search paths. Group size and activity pattern data were collected by walking along search paths and using instantaneous scan sampling. The broad habitat types identified were: Valley slope, Grassy slope, Ridge top flat, Nala slope, Valley bottom flat, Ridge top slope and Valley ridge slope. The vegetation types identified in the study area were: Sal forest (SF), mixed forest (MF), mixed forest grassy slope (MFGS), mixed forest riverine (MFR), sal forest riverine (SFR), pine-mixed woodland (PMW) and mixed forests with khai plantation (MFKP).The characteristic features of habitat and vegetation types and seasonal variations in them are discussed.The major findings of availability-utilization analysis were : Goral shewed preferential use of grassy slopes in summer. Valley bottom flat was used less in both the seasons. Mixed Forest was preferred in both seasons, whereas Mixed Forest Grassy Slopes were preferred only in summer. Sal Forest, Sal Forest Riverine and Mixed Forest with Khair Plantations were used less in both the seasons. A preferential use of the steep slopes was observed in winter. In summer there seemed to be no selection for terrain type. South facing slopes were preferred in both the seasons. Extremely low shrub cover and medium grass cover were selectively used by goral. Major features of goral group size and activity pattern were: Goral was predominantly a solitary species forming loose aggregations of upto eleven individuals. Average group size of goral did not vary significantly (N=230, d. f.=3, p=0.05, X" - 0.98) between seasons, but during late evening hours, comparatively larger groups were observed in winter (N=127, d.f.=4, p=<0.02, X2 - 12.42). Group sizes were comparatively larger in disturbed areas (N=230, d. f.=3, i i i p<0.01, = 12.75). A significant difference in proportion of time spent in different activities was observed (N=416, c/.f. = 8, p<0.001, X2 = 37.59), between winter and summer. Nevertheless, activities and proportions of active and inactive individuals varied significantly over different hours of the day (N=192, d.f.=2, p<0.01 , 10.43).Item Resource selection and resource partitioning among wild ungulates in the tropical semi-arid forest of Ranthambhore National Park. Rajasthan.(Wildlife Institute of India, Dehradun, 2001) Bagchi, Sumanta; Goyal, S.P.; Sankar, K.This study attempted to explore and describe the pattern of resource selection and inter-relationship in communal niche space of four species i.e. chital, sambar, nilgai and chinkara in dry deciduous semi arid forests of Ranthambhore national park, RajasthanItem Habitat Use by Rodents in a Sandy Habitat Around Sam, Western Rajasthan(Wildlife Institute of India, Dehradun, 1999) Mukherjee, Shomen; Goyal, S.P.Earlier studies on rodents in the Thar have recorded only the broad habitat types in which the different species occur. Except Rogovin el al. (1994), no other study has looked into microhabitat use by rodents. The present study aims to look at habitat use by three species of gerbils in a sandy habitat: The macro and microhabitat use by three species of rodents viz. Gerbillus gleadowi, G.nanus and Meriones hurrianae, in a sandy habitat, receiving rainfall of around 100-200 mm, was studied in Thar desert. Three distinct sandy habitats (Stabilized dunes Barren dune and Interdune), within 4 sq. km. area around Sam, Jaisalmer. was selected for the study. Due to zero captures after 500 trap nights, the use of Sherman traps was discontinued. Instead, circular track plots made out of chalk powder were used for looking at microhabitat use within each of the habitats. Track identification, up to species level, was first standardized from live specimens in captivity and then used in field. A total of sixteen variables representing habitat complexity (vertical), heterogeneity (horizontal) and phenology were enumerated around each plots. G. gleadowi was found to be the most abundant species, occupying all the three habitats. G. nanus was found to inhabit the Stabilised and Interdunal areas, while M. hurrianae was present only in the Interdune. Factor analysis using principle component extraction was used to determine the microhabitat characteristics. G. gleadowi was the sole occupant of Barren dune, where it did not show preference for any particular microhabitat. ' During winter, in Stabilised and Interdune, G. gleadowi was found using areas with relatively less compact soil, lower mean vegetation height and fewer number of hummocks compared to G. nanus. In summer, the species still continued using areas with relatively lower soil compactness, mean vegetation height and fewer hummocks compared to G. nanus, but showed higher use of areas with more ground cover (vegetation) compared to winter. G. nanus was found using areas with relatively more compact soil, higher mean vegetation height and greater number of hummocks. Overall, G. gleadowi was found to use the maximum range of microhabitats compared to the other two species. The summer niche space of G. gleadowi was found to be greater than its winter niche. During summer it was found using areas with more ground cover, higher percentage mature leaves, young leaves and fruits. M hurrianae was found to have a strict association with Capparis decidua tree, under which it burrows. The species is probably facing microhabitat loss due to collection of C. decidua poles by villagers.