M Sc Dissertation(WII)
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Item Relocation and Resilience : A Case Study from Sariska Tiger Reserve(Wildlife Institute of India, Dehradun, 2021) Abhishek; Baroth, Anju; Kolipakam, Vishnupriya; Qureshi, QamarRelocation of villages have implications on socioeconomic status of forest dependent people, however studies have often ignored the well-being of people after relocation. Sariska Tiger Reserve has undertaken relocation as one of its key programmes for biodiversity conservation. In my study I took a field work of analysing the ground realities of relocation in Sariska Tiger Reserve. The objectives of the study suggest: (1) documenting the perception of forest department and communities towards relocation. (2) analysing the resilience of communities in “Relocated” and “To be Relocated” sites. My study includes the use of sociological survey techniques including questionnaire survey, semi-structured interviews, observatory analysis, focused group discussion etc. The study was conducted in two relocated sites (1) Rundh Maujpur (2) Bardod Rundh and future projects villages for relocation Kankwari, Haripura, Lilunda and Kraska. 86 households were surveyed in relocated sites and 96 households were surveyed inside the core zone of Sariska. Results of Resilience have been quantified through abstract and non-abstract measurable. The finding in the study shows that, the influence of local inhabitants on relocation process is very limited. Forest department and local authorities need to retrospect their notion of conservation and rethink their plan for relocation.Item Effect of village relocation on ground birds and small mammals in Sariska Tiger Reserve, Rajasthan, India(Wildlife Institute of India, Dehradun, 2017) Mondal, Rakesh; Goyal, S.P.; Nigam, Parag1) Conservation related resettlement has been practised in India from 1960' s. However, studies related to the effect of village relocation on wildlife are limited. 2) Exploitation of natural resources by resident communities causes direct negative impact on native fauna and flora. These activities may include extraction of natural resources (fodder and fuel) or competition for the available resources by existing livestock with native fauna. Alterations in the vegetation structure can result in alteration of the bird community in these areas. 3) Galliformes is one such taxon that has been documented to be affected by human disturbance and grazing. These species are good indicators of habitat quality as they are solely dependent on the ground layer for food and cover. 4) There are 29 villages inside the Sariska Tiger Reserve and a relocation effort initiated as early as 1966 provides an excellent opportunity to study its effect on wild fauna and flora. 5) The study was carried out in four sites, with two sites where villages had been relocated 50 years (Slopka) and 10 years back (Bhagani); one site where village had been partially relocated (Sukola) and one where the village still existed The primary objective was to understand the influence of village relocation on Ggalliformes, small mammals and small carnivores. Additionally, vegetation structure at each village was also studied to understand influence of village relocation on natural vegetation.Item A Countryside carnivore: aspect of leopard ecology at Jawai, Rajasthan(Wildlife Institute of India, Dehradun, 2017) Sharma, Ravi Kumar; Qureshi, Qamar; Das, Abhijit1.Increasing human population and habitat fragmentation has impacted the large carnivore population across India. Leopard among pantherine is more tolerant to human disturbance and co-occur with humans in the wide variety of habitats. 2. Study was undertaken to understand status of leopard and factors responsible for its survival in human-dominated landscape. 3. Study was conducted in Jawai Dam Community Conservation Reserve from December 2016 to April 2017 in a semi-arid region of Pali, Rajasthan, India We examined villager's perception towards leopard by taking out the percentage of each response of respondents. Tolerance and religious view toward leopards was found significantly similar with each other, villagers has higher economic losses (livestock loss by leopards) than benefits (tourism activities) generated by hotel lobby. Villagers were examined to have minimal loss of human life and injuries by leopards, so it's easy to say about existence than co-existence or co-occurrence of both leopard and human in Proposed lawai Leopard Community Conservation Reserve.Item Habitat and Food Resources Use in Relation to Sex Age and Group Size in Sambar (Rusa unicolor) During Winter in Dry Tropical Deciduous Habitat of Ranthambore Tiger Reserve, India(Wildlife Institute of India, Dehradun, 2011) Goswamy, Amit; Goyal, S.P.; Sankar, K.The study of habitat use depends on various factors' like environmental conditions, resource availability, physiological condition of an animal and sex. The present research for my dissertation shows that it does exist and it attempts to explain how it is happening. Sambar is a major prey species of tiger and other big cats across most of the parks in India. For the conservation of large predators it is important to evaluate and study the habitat requirement of its major prey species in detail to the level of its age and sex categories. My field study was undertaken between Dec 2010 to March 2011. Intensive study area of 90 sq km was selected in Ranthambhore. to quantify resource availability and use by different categories with respect to sex, age and group size during winter. It was found out that there is a difference in the habitat use of sambar due to sex, age and group size categories, out of the many parameters evaluated and comparisons made it was seen that though in some cases the differences were not profound, and some showed only minor changes, but in majority of the cases the trend observed was as per the expectation. Where smaller body size male animals < 3 yrs) and female associated with fawn and subadults always prefer areas having a good quality resource whereas the adult male and sambar in large group size were mainly in the areas of abundant resource rather than the quality.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 Food habits of tiger (Panthera tigris tigris) in Sariska tiger reserve, Rajasthan(Wildlife Institute of India, Dehradun, 2003) Avinandan, D.; Sankar, K.; Qureshi, QamarThe present study aims at understanding relationship between tiger and its prey in a semi arid tract. The study was conducted in Sariska tiger reserve, Rajasthan over a period of six months from November 2002 to April 2003. Density estimation of major wild and domestic prey species was done to assess availability to tigers in terms of density and biomass. The line transect method was used to estimation prey densityItem Seasonal Change in Social Structure, Behaviour and Habitat Use by Sarus Crane in the Semi Arid Region of North-Western India(Wildlife Institute of India, Dehradun, 2001) Latt, Tin Nwe; Choudhury, B.C.The seasonal change in social structure and habitat use by sarus cranes was examined in the semi arid region of North- western India. The study was conducted in Keoladeo Ghana National Park and in the surrounding areas in Bharatpur district of Rajasthan. The methods involved censusing of cranes in the park and in surrounding areas by moving on motorcycle in preidentified routes. The detailed methodology included quantification of habitat availability and focal and scan sampling for studying the behaviour of sarus crane. Eight sarus groups were intensively monitored to examine parent and juvenile relationships and juvenile weaning process. The mean encounter rate of sarus crane outside the park was greater than that of inside. Though the data was not tested for the lack of uniform effort in these two areas, the difference is likely to be statistically significant. The overall group composition during the study period differed inside and outside of the park. The agricultural areas outside had greater number of social family group sighted during the study period than within the park. The mean encounter rates had greater standard errors associated with them outside the park than inside the park. During the present study most of the social family, pair, congregation, and solitary crane were seen outside of the park except that of pair with juvenile. The seasons (winter and summer) had an influence on the sarus crane group composition apart from the fact that the groups were either seen within the protected area or outside. With the data from the present study it is not possible to test the effects of these two variables on the sarus group composition. However, in winter sarus cranes were seen in social family and pair with juvenile more often inside the park than outside the park. The other forms of groups of sarus such as social group, pair and solitary members were not very different inside and outside the park. In winter season, juveniles were not able to fly more than 0.61 m height and 45m distances restricting their movements within the park. During summer the juveniles could fly outside of the park in the 1st week of February onwards and were seen frequently outside of the park. Sarus cranes spent more time outside the park than inside, except pairs with juveniles. Inside the park the safety, food and space supported small groups and pairs all through the year. The group composition showed a dramatic change in summer where greater number of social family and pair with juveniles were observed outside the park than inside, while other forms of groups did not vary much in the two areas. During the study period a maximum of 67 sarus cranes were recorded inside the park in roosting areas. During the study period, wetlands were the most used habitat by sarus cranes than any other habitat types. Grasslands and dry wetlands were used distinctly by sarus next to the wetlands, and the agricultural fields have the least utilization. The later could be because of bias in sampling more inside the park than in the agricultural fields outside the park. During summer, the sarus cranes occurred more often in wetland and grasslands than in dry wetland or agricultural fields. During winter and summer sarus cranes mostly used wetland habitat (winter 20.5 % & summer 35%). In late summer, as all agriculture field were harvested and there was no water patches outside the park. The Forest Department pumped in water throughout the late winter and summer in the areas where group no (Block L), group no.4 (Block D) and group no.5 (Block E) spent more of their time. During summer, sarus cranes used this shallow water. The area where group no.3 (Block K) sarus stayed much of the time had very large grasslands. Within this area the wetland was closer to road and sarus crane appeared to be stressed while foraging in this wetland. The large expanse of grasslands used by group no. 3 (Block K) area, it prevented people to approach closer to the cranes and hence they used this grassland extensively during summer. Among the pair, the female was more the wary and cautious while using these water patches. Solitary sarus cranes preferred foraging in grasslands. In summer, water spread became small and narrow and sarus cranes spent more time in grasslands (winter 5% & summer 12%). Sarus crane did not use dry wetlands in summer due to lack of moisture in this area which, hinders growth of grasses and other aquatic flora and also insects in such dry wetlands were less. Generally, sarus crane used agriculture land more for foraging at the time of sowing and harvesting of cereal and pulses. The encounter rates (sightings/ hour) of sarus crane correlated with water level. During large water spread times, more cranes were encountered. Water depth was correlated with mean encounter rates (r= 0.77, N= 1 Z) , similarly water spread also had a significant positive correlation (r=0.64, N= 12). As expected water depth and water spread had a strong positive correlation (r=0.95, N= 12). At the beginning of the study in November the juveniles were estimated to be three months old, and when the study was concluded in May, the juveniles were nine months old and they continued to remain in the vicinity of the parents. Although the distance increased with time it is speculated that the quantum of time spent by the adults parenting the juvenile would diminish with time and also the distance between parents and juveniles. The major interaction between parent and juvenile during the observation period was "nursing" behaviour, where the parent fed the juvenile directly into its mouth. Subsequently, the parent "induced the juvenile to forage" by leading the juvenile to some areas in the wetland where food was abundant and the disturbance from tourists was low. From the last week of February juvenile started to move farther away from the parents and maintained an average distance of about 65 m. During this time the parents started courtship behaviour and paid less attention to the juveniles, even though the juveniles showed interest on their parents. In reciprocation of the lack of attention from the parents the juveniles continued to forage away from the parents. Till the end of the study period in May the juvenile still continued to tag along with the parents. To summarize, seasonal shift in sarus crane social structure was observed in the study area. Following factors appear to affect the sarus crane group structure and behaviour: (a) Availability and limitation of food.(b) Changes and availability of water in wetland. (c) Age of juveniles appears to be a factor for their attachment to parents.(d) The diurnal weather appears to be relative to sarus crane behaviour and social structure,which change on cloudy, sunny and rainy days .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 Food habits and foraging behaviour of Indian Gazelle (Gazella benneti) in Rajasthan desert(Wildlife Institute of India, Dehradun, 1997) Kodoth, Ganesh; Goyal, S.P.The Indian gazelle inhabiting the arid regions is studied with respect to their food habits and foraging behaviour. In arid areas the selection of a habitat by an animal is mostly governed by spatial and temporal distribution and abundance of food items and the food requirements of that species. This becomes critical especially in an semi-agricultural landscape where the ecosystem is altered without any consideration for the animal. The study was conducted in a habitat close to human habitation around Jodhpur after the harvest. This area is dominated by desert vegetation such as Crotalaria burhia. The study is conducted for a period of six months encompassing two seasons winter (December 15, 1996 - February 20, 1997) and summer (March 20, 1997 - May 10, 1997). The intensive study area was differentiated into six habitat types based on the structural and floristic composition of the vegetation-viz, crop fields, fallow lands, scrub area dominated by Zizyphus, and hedges of Maytenus-Capparis Zizyphus among the agricultural fields. Differential habitat selection by gazelle was observed during summer and winter mainly due to selection of diet based on seasonal nutritional requirements. Diet selection is looked in terms of use-availability and plant chemistry. Based on a relative preference ratio, the habitat and food types were ranked, and the observed trends are explained in terms of the existing theories on diet selection. Diet composition varies with the age and sex classes of the animal viz. breeding males, sub-adult males and adult females. In winter and summer differences in habitat use was exhibited by gazelle, also there was a difference in proportion of the food species in the diet between two seasons. The scrub area was dominated by vegetation having higher crude protein and tannin, was used more than, available in order to supplement their diet (especially in the case of , females) and in summer the crop fields dominated by Crotelaria burhia were used more by all categories of animals. Females fed on a high protein and less tannin diets which is pronounced in winter, sub-adults also fed on a diet having higher protein and tannin, while males were not biased towards a high quality food both in winter and summer. These differences were influenced by the spatial distribution, of food species, plant chemistry, and the differential use of food species among different age and sex classes during the two seasons. Protein and tannins along with moisture seem to govern diet selection rather than just being a function of availability during winter and summer. Spatial distribution of food plants along the habitat types (in the current land-use pattern) does influence habitat use by gazelle. Selection and proportion of the time spent on food species during summer and winter suggest that Indian gazelle is a browser.Item The Diel Activity Pattern of Indian Python (Python molurus molurus linn) at Keoladeo National Park and Some Factors Influencing it(Wildlife Institute of India, Dehradun, 1991) Bhatt, Karamvir; Choudhury, B.C.This study investigated die] activity pattern of Indian python (Python moJurus molurus Linn) at Keoladeo National Park Bharatpur. The study was conducted in an intensive study area of 0.5 Sq Km selected after pre sampling survey in the park. The methodology involved to estimate activity pattern of pythons was monitoring of a permanent transect every four hours, on diel basis, to record python’s tracks and sightings. The diel variations in temperature, humidity, burrow microclimate, prey activity and prey abundance were also quantified along with diel activity pattern of python. Results show a shift in diel activity pattern with seasons. The activity pattern of pythons was diurnal in winter, uniform throughout spring and bimodal crepuscular in summer. There was no significant correlation between python activity and other factors quantified, though temperature and humidity affected the diel activity pattern considerably. The microclimate variation gradient existing between outside and inside burrow possibly play an important role in occupation of the burrow and this in time influence the surface diel activity pattern. The shift in the diel activity is attributed to seasonal change in the abiotic factors. No relationship between prey abundance and activity pattern could be established possibly because python’s ability to go with out food during the cool season. Other factors not quantified during this study like reproductive behavior, body size and biotic disturbances are suspected to be responsible for the observed diel activity pattern of pythons. It is concluded that the diel activity pattern of pythons in KNP is not influenced by just one factor but is a manifestation of a combination of various abiotic, biotic and endogenous factors. A temperature sensitive telemetry study would help further in investigating the ecological aspects of this cryptic species.