Theses and Dissertations
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Item The feeding ecology of the Dhole or Asiatic Wild Dog (Cuon alpinus) in Kanha Tiger Reserve, Madhya Pradesh.(Wildlife Institute of India, Dehradun, 2008) Acharya, Bhaskar B.; Johnsingh, A.J.T.; Sankar, K.In order to collect basic information on the prey species of dholes, this study aimed to estimate the density, encounter rates, biomass, and the population structure and composition of the major prey species within the study area. Eventually, The objective of this study was to determine the relative proportions of different prey species in diet of dholes, in terms of frequency of occurrences, biomass, and numbers of individuals consumed. The aim was also to study predation by dholes in relation to prey availability and utilization within Pench Tiger Reserve, i.e. to see if dholes killed prey randomly or selected specific kinds of prey. If that was so, the ecological factors intrinsic to that prey which may influence prey selection were assessed.Item Behavioural ecology of sloth bear in Panna National Park, Central India.(Wildlife Institute of India, 2005) Yoganand, K.; Johnsingh, A.J.T.The patterns in daily and seasonal activity of sloth bears in Panna NP were studied and the factors that influenced the patterns were assessed. • Activity states were recorded by manually monitoring radio-tagged, motion-sensor fitted bears, and by deploying automated receiver-recording units that logged the strengths and pulse rates of signals from the bears. Daily and seasonal changes in temperature, relative humidity and other heat indices of the microhabitats used by bears were recorded using temperature and RH loggers. Tiger and human activities were also monitored to assess the influence of these on bear activity patterns. • Bears were found to be essentially nocturnal and crepuscular in activity and they rested during midday. This pattern of activity was similar among all radio collared bears, but with some variability. The differences in diel activity patterns among climatic and fruiting seasons were rather small. In the wet and cold seasons, bears extended their activity into the day hours and reduced their activity in post-midnight, pre-morning hours, as compared to the dry season. • Bears (except the cubbing females) were active almost every day of the year, and for several hours (> 10 hours) each day. Overall, bears were active for 48% to 54% of the whole day (out of 24 h) in all seasons. There were no large differences seen among months in percent of whole day, day time, night time, and morning time the bears were active, but evening time showed large differences. • The differences in activity start and end times among individual bears within seasons were large in certain seasons, and the differences among seasons of a bear were large for certain bears. Bears such as F63, F78 and M69 did not show much difference among seasons, while others such as F76, F80 and M50 showed large differences. Also many bears showed higher variability in cold and wet seasons than in dry season, particularly in activity start times. • Bears started their activity later and ended it earlier in the dry season than the other two climatic seasons. The earliest activity start and latest activity end was in the cold season. The differences among climatic seasons in both timings were statistically significant (ANOVA, α = 0.05). However, when activity start and end times were adjusted for seasonal sunset and sunrise times, the patterns in seasonal differences changed remarkably. 109 Wet season activity start times with reference to sunset were much earlier than the other two seasons, whereas the difference between cold and dry seasons became small. Differences in activity end times after sunrise between cold and the other two seasons too became small. • Escarpment habitat was most frequently used (50% to 85%) for day resting by bears in all months, followed by Lantana shrub thickets (15% to 50%). The use of escarpment was predominant in dry season months and decreased in monsoon and post-monsoon months, with a converse increase in the use of Lantana habitat as day-bed. • The core bears, which had substantial escarpment habitat available within their home ranges, used escarpments for day-resting predominantly in all seasons, and the peripheral bears, which had low escarpment and high Lantana cover available, used these habitats for day-resting variably. Tigers were generally nocturnal and crepuscular in activity during the dry and cold seasons. The activity of tigers peaked during crepuscular times; they predominantly rested during mid-day, and had a reduced level of activity during post-midnight, pre-morning hours. • Diel activity patterns of bears and tigers were similar to a large extent, in the two seasons tigers were monitored. The activity peaks of both species more or less coincided in the mornings and evenings, and high levels of activity of both occurred in night and crepuscular times. • Tiger activity does not seem to influence bear activity timings. The hourly activities of both were strongly positively correlated, even after controlling for temperature, with which bear activity was strongly correlated. • Humans using the forest habitats showed a high level of activity in the morning and evening times, moderate level of activity in the mid-day, early morning and late-evenings, and a low level of activity in the immediate premorning and early night hours. • Human activity overlapped highly with that of bear activity during early morning and evening hours. Overlap period was longer and the activity peaks of both coincided in the evenings of wet and cold seasons. No relationship could be seen between their hourly activitiesItem Habitat use by sympatric small carnivore in Sariska Tiger Reserve, Rajasthan, India.(Wildlife Institute of India, Dehradun, 1998) Mukherjee, Shomita; Johnsingh, A.J.T.The present study on three sympatric carnivores, two felids: jungle cat (Felis chaus), and caracal (Caracal caracal) and one canid, the golden jackal (Canis aureus) aimed at studying their spatio - temporal use of food resources. The hypothesis are as follows : 1) Jungle cat is relatively more eclectic in the kind of habitat it inhabits than the jackal. 2) The felids are mostly nocturnal whereas the jackal is both diurnal and nocturnal ( cathemeral). 3) Diet of the three carnivores differs between seasons. 4) Small mammals «1 kg. body weight) form the major diet of the felids and are taken in proportion to their abundance. 5) Jungle cat and caracal are dietary specialists relative to the jackal. The study was conducted in Sariska Tiger Reserve (STR) which is located between 74° 17' to 76° 34'N and 25° 5' to 27° 33' E. STR encompassing an area of BOO km2 has three core areas of which core 1, with an area of 273.B km2 forms. the proposed National Park. This area functioned as the study site and the intensive study area was approximately 30 km2.Item Feeding Ecology of Ibex (Capra ibex sibirica) in Pin Valley National Park, Himachal Pradesh.(Wildlife Institute of India, Dehradun, 1997) Manjrekar, Neema; Johnsingh, A.J.T.The foraging ecology of the Asiatic ibex was studied in Pin Valley National Park Lahul and Spiti District, Himachal Pradesh, between October 1991 and October 1994. The National Park encompasses 675 km2, and has a buffer of 1150 km2. The study area constituted part of the Parahio catchment of the pin Valley. Thango was the base camp for this study. It was a summer settlement of five families from Sagnam, the largest village of Pin Valley. The local people are Buddhists, of Tibetan origin. Apart from cultivating the land adjacent to the villages, in the buffer zone, they use the Park area for cultivation of barley, wheat, peas, mustard, and potatoes. They also graze sheep, goats, yaks, horses and donkeys in the area. Fuel wood, and fodder for stall-feeding, is collected from the Park before winter. Two potential conservation threats to ibex were identified. Firstly, migratory livestock from the neighbouring areas use the area between June and August every year. ' There is no control on the numbers of animals entering the area, and the effects of grazing and trampling need to be quantified.Item Ecology of the Asiatic Lion Panthera leo persica.(Wildlife Institute of India, Dehradun, 1993) Chellam, Ravi; Johnsingh, A.J.T.The major objectives of my study were to assess the predation ecology, habitat use and the ranging patterns of the lions in the Gir forest. The ultimate and long term goal of this research effort was to examine the feasibility of a translocation effort in an attempt to establish a free ranging population of lions away from the Gir forest. The ecological data generated a free ranging population of lions away from the Gir forest. The ecological data generated would enable the assessment of prospective translocation sites and insights gained about lion behavoiur. This study was designed to have an extensive scope to generate base line data for planning and management of gir forest and the lions.Item Habitat Ecology of major ungulates in Kedarnath musk deer sanctuary, Western Himalaya.(Wildlife Institute of India, Dehradun, 1994) Sathyakumar, S.; Johnsingh, A.J.T.Present study on the habitat ecology of major ungulates in Kedarnath Wildlife Sanctuary "(WS) was conducted from March 1989 to November 1991. The objectives of this study were to de,!elop suitable techniques for estimating ungulate abundance and density; to study their habitat utilization pattems; and to assess the status of ungulates and their habitats in different parts of the Kedarnath WS.Item Ecology and Management of Lion and ungulate habitats in Gir.(Wildlife Institute of India, Dehradun, 1995) Sharma, Diwakar; Johnsingh, A.J.T.The Gir is the only refuge of the Asiatic lion (Panthera leo persica) in its range. This implies that long term conservation of the Asiatic lion will remain an overirding management objective. A study on the impacts of management practices on lion and ungulate habitat was conducted in Gir Protected Area (PA) from June 1991 to July 1994. The Gir . PA includes Gir Wildlife Sanctuary and National Park. It is situated between 200 55' to 21 0 20 'N and 700 25' to 71 0 15' E in the Southern part of Kathiawar peninsula in western Gujarat. Gir PA (hereafter Gir) is located about 60km South of Junagadh. The area which was .3,107 sq km iIi 1877 (Joshi 1976) has been presently reduced to 1,412 sq km, o~ which about 259 sq Ian is national nark. Gir is the last refuge of the wild Asiatic lions (Panthera leo persica) and long term conservation of the Asiatic lion is an overriding management objective of Gir. In order to improve habitat conditions in Gir, the park authorities, over the last 20-25 years have made some management interventions such as relocation of some maldharis (local graziers), reduction in livestock grazing (specially migrant livestock during the rainy season) and fire control. These measures have led to vegetational recovery and increase in wild ungulate and lion populations. Understanding this vegetational recovery was thought to be crucial to determine the extent of management intervention required. It also needed to be determined if the trend (especially in the western Gir) was toward a higher woody proportion both at shrub and tree levels, and whether this in long term would adversely affect ' the distribution and abundance of ungulates, and therefore, group hunting by the lions, their pride size and territoriality.Item Habitat Use by Goral (Nemorhaedus goral bedfordi) in Majhatal Harsang Wildlife Sanctuary Himachal Pradesh, India(Wildlife Institute of India, Dehradun, 1993) Mishra, Charudutt; Johnsingh, A.J.T.Studied the habitat use pattern of goral (Nemorhaedus goral bedfordi} in Majhatal Harsang Wildlife Sanctuary in the Himalaya to determine its habitat requirements. Of special interest were the roles of forage availability and quality and the antipredator strategy of goral in determining its habitat selection. These factors are of paramount importance in influencing the habitat selection by mountain ungulates. Diet composition of goral in terms of the proportions of graminoids versus browse was determined through pellet analysis. Its escape strategy was determined by direct observation. These results were then related to the actual habitat use patterns, which were determined by obtaining and quantifying locations of goral (n=334) over two seasons, along five monitoring trails. Use of each habitat category was interpreted with respect to its availability. A non-mapping technique was used for determining the availability of each habitat component. I identified nine vegetation types based on physiognomy and floristics. These were: Open Pine Community (OPC), Dense Pine Forest (DPF), Open Oak-Pine Community (OOPC), Dense Oak-Pine Forest (DOPF), Nullah Oak Forest with Low undergrowth (NOFL), Nullah Oak Forest with High undergrowth (NOFH), Euphorbia-Woodfordia-Dodoenia Scrub (EWDS), Open Euphorbia Scrub (OES) and Low Altitude Nullah Forest (LANF). Both forage quality and the antipredator strategy had a profound influence on habitat selection by goral. Goral was a grazer. It was partial to the younger, more nutritive grass phenophases - a prediction that can be made on the basis of its small body size. It preferred open areas with extensive grass cover. Forest cover, along with cliffs, was an important escape area for goral. But it avoided areas with extensive shrub cover. Such areas have little grass. Besides, the shrub cover obstructs visibility and quick movement, and makes the animal vulnerable to predation.Item Social Behaviour and Communication Among Wild Lion-Tailed Macaque (Macaca silenus) in the Indira Ganghi Wildlife Sanctuary, Tamil Nadu(Wildlife Institute of India, Dehradun, 2001) Raghavan, Roopali; Gupta, A.K.; Johnsingh, A.J.T.This study on the social behaviour and communication among wild lion-tailed macaque was carried out between November 2000 and April 2001, on a group of lion-tailed macaques that inhabit the wet evergreen Puthutotam forest fragment. located within the Indira Gandhi Wildlife Sanctuary in the Anaimalai hills, Tamil Nadu.The troop consisted of 16 to 19 animals. For the purpose of this study, social interactions within and between adults and subadults of both sexes were considered. Focal animal sampling and instantaneous scan sampling was thus conducted on only ten identified individuals (four males and six females) in the troop. A complete ethogram describing all behaviour observed during the period of the study was repared. The time-activity budget was calculated for the troop. The predominant behavioural states among all the individuals were Active Forage (mean ± SD of 22.4 ± 0.08%), Active Feed (17.0 ± 0.05%), Sit (16.6 ± 0.04%), Move (13 ± 0.030/0), Passive Forage (6.8 ± 0.02%) and Passive Feed (6.5 ± 0.02%). The adult males and females of the study troop differed in the proportion of time spent by them in the different behavioural states. Autogroom and Allogroom accounted for the principal difference between the sexes. Adult males spent relatively greater time Autogrooming than females, while females allogroomed relatively more. Dominance ranks were calculated independently for males and females in the study troop. Among both males and females, rank position in the dominance hierarchy appeared to be influenced strongly by body size. This is an unusual finding for the females of cercopithecine primate species, implying the existence of an unique individual-based dominance hierarchy among the study females. There was i.e remarkable similarity in the frequency with which dominant and subordinate females displayed virtually all behaviours towards each other in dyadic interactions. This provides support to the prevailing view that lion-tailed macaques indeed display an egalitarian nature. Classification of the gestures and vocalisations were observed to be largely dependent on the dominance rank of the individuals. with certain gestures being characteristic of submission. Males and females showed differential use of the gestures and expressions.Item Density, Biomass and Habitat Occupancy of Ungulates in Bhadra Tiger Reserve, Karnataka(Wildlife Institute of India, Dehradun, 2001) Jathanna, Devcharan; Johnsingh, A.J.T.The distribution and abundance of ungulates prey of tiger were studied in the tropical moist deciduous forest of Bhadra Tiger Reserve, Karnataka from November 2000 to April 2001. The species of interest were chital, sambar, Muntjac and gaur. The line transect method was used to estimate absolute densities of the study species in November 2000. Distribution of the study species was studied using dung as an indicator of occupancy. Logistic regression models was used to examine species presence/absence and habitat parameters.