Certificate - Etheses - Saurashtra University

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iver and streams, Exposed rocks with slope grasses, Agricultural land and Grassland and forest blanks. The steep slope terrain was used by bear only in Mixed forests with conifers and broad leaf species, Grassland and forest blanks and Himalayan moist temperate forest with conifers. In Kugti wildlife sanctuary, the differential use of terrains in various habitat types could be related to factors like availability food, resting, seeking shelter, escape cover and biotic disturbance. As observed in field areas, bears might be using flat terrain in Agricultural land and Grassland and forest blanks, Mixed forests with conifers and broad leaf species and Exposed rocks with slope grasses maximum for feeding on herbaceous plants, insects and ants, and also for killing livestock and feeding on them. They might also be using this terrain for resting. All the habitat categories in gentle slope terrain were found to be used differentially presumably for seeking food and shelter and resting activity. The use of Moist sub-alpine scrub characterized by Rhododendron species and Dry alpine scrub characterized by Juniperus species habitats in different terrains could be mainly for shelter and escape cover. Whereas the use of Near water bodies, river and streams and Riverine forest habitats in undulating and gentle slope terrains by bears might be for food, water requirement and movement from one area to another. Brown bears might be using Mixed forests with conifers and broad leaf species, Grassland and forest blanks and Himalayan moist temperate forest with conifers habitats in steep slope terrain mainly for seeking food and their requirement. When the proportional availability of various terrain types was compared with the expected use of these terrains by brown bear, the proportional availability of gentle 98
slope terrain was found to be highest, followed by flat terrain, undulating terrain and steep slope terrain. Similarly the expected use of these terrain types was found to be directly proportional to the availability. The expected use of gentle slope terrain was found to be highest, followed by flat terrain, undulating terrain and steep slope terrain. There was no difference between the proportional availability of terrain types and expected utilization of each terrain within the study area. So the proportional availability of various terrain types was found to be directly proportional to the expected use of the terrain. 99
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Saurashtra University Re - Accredit
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Ecology of brown bear (Ursus arctos
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Contents Acknowledgements i-iv Summ
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List of Tables Chapter 4: Feeding e
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Figure 5. Presence of food items in
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Photograph 11. Collection of brown
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ACKNOWLEDGEMENTS Several individual
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logistic support in the alpine and
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Summary The brown bear is widely di
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own bears and seasonal difference i
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use of these habitat categories. Si
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Chapter 1 1.1 Bear species and dist
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Hokkaido, the Hokkaido brown bear (
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1.2 Status of bear species All bear
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human beings. The resources availab
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protection methods have been studie
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viii. The study will also help sugg
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Brown bears were found tetrapedal,
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hence created their own dens. Brown
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2.5 Habitat use pattern Johnson (19
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evealed that although both preferre
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Marchinton, 1980; Smith, 1986; Hell
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and ground nesting birds and their
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kelp, mollusks, fish and remains of
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during early summer (Hamer and Herr
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1983a). Although insects constitute
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fruits and mammals. Their study als
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geographically (LeFranc et al., 198
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commodities in their search for alt
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Yellowstone National Park between 1
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ear-livestock interactions were rep
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Gamgul Siabehi are relatively less
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A list of angiosperms and gymnosper
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(Ursus arctos), the other wild anim
Page 69 and 70: Chapter 4 Feeding ecology of brown
Page 71 and 72: 1984; Mace and Jonkel, 1986; Odhach
Page 73 and 74: these scats were separately placed
Page 75 and 76: were analysed, and the proportion o
Page 77 and 78: Fragaria nubicola 34 times. Photogr
Page 79 and 80: Figure 5 showed marked monthly vari
Page 81 and 82: the method of percent occurrence of
Page 83 and 84: (Hedysarum alpinum) roots and main
Page 85 and 86: and Aoi, 1987). The higher occurren
Page 87 and 88: constituted a major portion of earl
Page 89 and 90: Figure 2. Frequency occurrence of a
Page 91 and 92: Continued Food items Occurrence Sum
Page 93 and 94: Figure 4. Number of direct feeding
Page 95 and 96: Table 3. Availability of food items
Page 97 and 98: Table 2. Number of direct feeding o
Page 99 and 100: omnivorous generalist lifestyle. Br
Page 101 and 102: systematic information is available
Page 103 and 104: 5.3.0. Results In Kugti wildlife sa
Page 105 and 106: for Agricultural land category and
Page 107 and 108: 5.3.3 Habitat availability vs. util
Page 109 and 110: ocks with slope grasses (38.4%), Mi
Page 111 and 112: gentle slope terrain was found to b
Page 113 and 114: Exposed rock with slope grasses and
Page 115 and 116: found mainly dependent on availabil
Page 117 and 118: availability of brown bear habitat
Page 119: Ballard et al., 1993) and interior
Page 123 and 124: Table 1. Continued S. No. Dry alpin
Page 125 and 126: Table 3. Frequency of occurrence of
Page 127 and 128: Table 5. Seasonal variation in habi
Page 129 and 130: Table 7. Proportional availability
Page 131 and 132: Figure 1: Sampling layout for veget
Page 133 and 134: livestock and attack on people. In
Page 135 and 136: 1978; Knight and Judd, 1983; Garshe
Page 137 and 138: develop mitigation strategies that
Page 139 and 140: division, Chamba wildlife division,
Page 141 and 142: in the sanctuary area. Figure 1 als
Page 143 and 144: Different plant species, phenologic
Page 145 and 146: Damage to wheat crop was 15-25%. Ma
Page 147 and 148: Ghiula dhar, Bharali Kinnaur dhar,
Page 149 and 150: Livestock depredation by brown bear
Page 151 and 152: The studies conducted in India and
Page 153 and 154: Table 1. List of grazing pastures o
Page 155 and 156: Table 3. Livestock depredation in d
Page 157 and 158: Figure 1. Livestock depredation in
Page 159: Table 5. Agricultural crops and the
Page 162 and 163: Table 7. Damage to agricultural cro
Page 164 and 165: 7. Suggestions and recommendations
Page 166 and 167: 4. In Kugti wildlife sanctuary, the
Page 168 and 169: During evening and night time, the
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17. Brown bears cause extensive dam
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References Abe, H., Aoi, T., Tsubot
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Aune, K. and Kasworm, W. (1989). Fi
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Berns, V.D., Atwell, G.C. and Boone
Page 178 and 179:
Chauhan, N.P.S. (2003). Human casua
Page 180 and 181:
Craighead, F.C., Jr. and Craighead,
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Elgmork, K. and Kassa, J. (1992). F
Page 184 and 185:
Garcia-Gaona, J.F. (1997). Damages
Page 186 and 187:
Gunther, K.A. and Renkin, R.A. (199
Page 188 and 189:
Herrero, S. (1978). A comparison of
Page 190 and 191:
Irving, L. and Krog, J. (1954). Bod
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Joshi, A.R., Garshelis, D.L. and Sm
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Krishna Raju, K.S.R., Krishna Murth
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Mace, R.D. and Waller, J.S. (1996).
Page 198 and 199:
Mattson, D.J. and Hovey, F.W. (1995
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Mertzanis, G. (1994). Brown bear in
Page 202 and 203:
Nawaz, M.A. (2007). Status of the b
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Pazhetnov, V.S. (1990). Brown bear.
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Reynolds, D.G. and Beecham, J. (198
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Sathyakumar, S. (2006a). The status
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Sellers, R.D. and Aumiller, L.D. (1
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Stein, J.T. (2000). From exterminat
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Van Daele, L.J. (1995). Unit 17 bro
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Yamanaka, M., Yasue, K. and Ohtaish
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Continued S. No. Common name Genus
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Appendix 3. GPS location of line tr
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Appendix 4 Format - 1(a) Vegetation
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Format - 1(c) Vegetation Compositio
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Format - 1(f) Biotic Pressures Tran
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Format - 2(b) Distribution and Abun
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4. Occupational Pattern: i. Noumber
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vii. Crop damage month-wise: Tick m
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E. NTFP collection: Name Species Qu
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