Certificate - Etheses - Saurashtra University

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Agricultural crops: wheat, maize, barley, phulan, bharesh, rajmash and vegetable crops were grown in Tendei, Dalautu, Seri, Bharmani and agricultural lands near lower Kugti and upper Kugti village on rotational basis in different years. As already stated that all agricultural crops were found to be damaged in this area, but the quantum of damage varied considerably in different agricultural lands depending on their locations. Agricultural crop field adjacent to forest and far away from the village suffered greater losses than the crop fields located near the village. Maize crop suffered highest level of damage by brown bears mainly because of food preference. Highest level of damage was recorded in Seri agricultural land, which was located about 2 km far from Kugti village, and it was difficult to protect the crop especially during night time. Damage to wheat crop was maximum in Tendei agricultural area, which was located at higher altitude, far away from the village. Likewise damage to barley crop was maximum in Dalatu agricultural land, which was about 3 km from the village. There was considerable damage to phulan crop in Tendei, Dalatu and Bharmani agricultural lands. All these agricultural areas were located far away from the village and crop raiding by brown bears occurred in the evening and night time. Bharesh crop also suffered maximum damage in Tendei and lower Kugti village. Agricultural crop rotation has been a common practice in Kugti village. By following this pattern, crop damage by bears could be substantially reduced as 75% of land holdings were situated more than 2 km away from the village and nearer to the forest where bears could easily raid agricultural crops especially during night. Among horticultural crops, brown bears were found to damage peach (Prunus persica) and jamu (Prunus cornuta) everywhere in the sanctuary area. 130
Table 1. List of grazing pastures or dhars in Kugti wildlife sanctuary. S. No. Name of the dhars 1 Andarli Dhamel dhar* 2 Andarli Kinnaur dhar* 3 Bharali Dhamel dhar 4 Bharali Kinnaur dhar* 5 Bhiad dhar* 6 Bhug dhar* 7 Bhumkar dhar* 8 Buhar dhar 9 Duggi dhar* 10 Dhugdhar 11 Gan dhar 12 Ghadoi dhar 13 Ghei dhar* 14 Ghiula dhar 15 Gufai dhar 16 Hali dhar 17 Jousaha dhar 18 Karog dhar 19 Mundi dhar* 20 Nanaun dhar* 21 Sarni dhar * 22 Siya dhar * Dhars selected for the conflict study 131
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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
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Chapter 4 Feeding ecology of brown
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1984; Mace and Jonkel, 1986; Odhach
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these scats were separately placed
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were analysed, and the proportion o
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Fragaria nubicola 34 times. Photogr
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Figure 5 showed marked monthly vari
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the method of percent occurrence of
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(Hedysarum alpinum) roots and main
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and Aoi, 1987). The higher occurren
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constituted a major portion of earl
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Figure 2. Frequency occurrence of a
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Continued Food items Occurrence Sum
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Figure 4. Number of direct feeding
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Table 3. Availability of food items
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Table 2. Number of direct feeding o
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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
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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 and 120: Ballard et al., 1993) and interior
Page 121 and 122: slope terrain was found to be highe
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: The studies conducted in India and
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
Page 170 and 171: 17. Brown bears cause extensive dam
Page 172 and 173: References Abe, H., Aoi, T., Tsubot
Page 174 and 175: Aune, K. and Kasworm, W. (1989). Fi
Page 176 and 177: 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,
Page 182 and 183: 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
Page 192 and 193: Joshi, A.R., Garshelis, D.L. and Sm
Page 194 and 195: Krishna Raju, K.S.R., Krishna Murth
Page 196 and 197: Mace, R.D. and Waller, J.S. (1996).
Page 198 and 199: Mattson, D.J. and Hovey, F.W. (1995
Page 200 and 201: 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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