M Sc Dissertation(WII)
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Item Assessing the Impacts of Road Network on Wildlife Corridors and Mitigation Measures in Assam : Transportation Against Animal Corridor(Wildlife Institute of India, Dehradun, 2021) Borgohain, Roshme; Habib, Bilal; Ramesh, C.Protected Area Networks (PA) and Conservation Areas (CA) are very essential for ensuring the conservation of wildlife. However, the connectivity among these protected areas is much more important to ensure the viable population of species. Furthermore, the increase in infrastructural development and human encroachment leading to the fragmentation of forests and the natural habitat of wildlife species. The wildlife corridors are the essential structures to connect the fragmented areas, ensure the viability of the isolated population, restores the genetic variations, corridors also increases the habitat diversity in the two habitat patches that it connects, it provides a passage for migration and also acts as an escape route in cases of fire in one patch. Overall wildlife corridors are structures that are important for conservation. Although these protected areas were not well connected the corridor structures help to maintain the continuity of the area. The state falls under North-East India Biogeographic zones under the Province North-East-East-Brahmaputra Valley (9B), (Rodgers and Panwar 1998). In Assam, there are seven National Parks and twenty Wildlife Sanctuaries occupying the area of 3925+ sq. km, where two are designated as World Heritage site (WHS) which is the highest designation given to the protected area. Out of twenty-seven protected area in Assam, fifteen were bifurcated by road networks and there are total eleven corridors, connects the protected areas, eight corridors were cut at multiple places by roads. These connections of the corridors are essential to maintain the contiguous landscape, which is further essential for maintaining the integrity of the WHS. In this study, I have tried to look at the current status of the wildlife corridor portion bifurcated by the road networks in Assam. The objective of the study is 1) What is the extent of different types of road networks concerning PAs and corridors in the State of Assam? 2) What is the land use pattern near the corridor bifurcated by the road? 3) Characterize the current status of the corridor sites impacted by the road network.Item Montane Lizard in a Mosaic Landscape: Effect of Tea Plantations on Anamalai Spiny Lizard (Sales anamallayana)(Wildlife Institute of India, Dehradun, 2021) Devrajan, Anjitha; Ramesh, C.; Das, AbhijitThe Anamalai Spiny Lizard (Salea anamallayana), an agamid lizard endemic to southern Western Ghats is reported to use shola and tea plantations of Kannan Devan hills of high ranges of Kerala. The Western Ghats has experienced extensive habitat destruction and modification since a very long time and the lizards are highly affected by habitat modification which in turn affect their fitness and survival. In this study we investigated the effect of habitat modification on morphology, population and habitat association in Salea anamallayana in the shola forests of Eravikulam National Park and surrounding tea plantations. The study was conducted from February 2021 to May 2021. Line transect method was used to study density and Visual encounter surveys for collecting data for basking habitat use and morphology. Surveys were conducted from 9 am to 2 pm since the lizard was more active during the time period. Shola and plantation are structurally very different. Shola was divided into shola close to plantations and shola away from plantation. Plantation was classified according to the proximity to shola and presence of shade trees. The density was found to be more in shola (27.59±6.79/ha) compared to plantation (8.63 ±2.21/ha). In plantations, the density was influenced by proximity to shola and presence of shade trees. Density is more in plantations in close proximity to shola (20.91±4.51/ha) compared to plantations away from shola (2.85±1.37/ha) and the lizard was present only where the shade trees were planted. The sex ratio was biased towards male in plantations (100:14) and it improves in shola close to plantations (100:33) and further improves in shola away from plantations (100:50). The body condition of male lizards was poor in plantations compared to shola away from plantations (t = 2.57, df = 14.17, p-value = 0.021). The males do not differ in other morphological variables across the habitats. Body condition of males is better than females (t = -2.19, df = 23.80, p-value = 0.037). The basking habitat use is in proportion to habitat availability. The microhabitat use varies across shola and plantation. Average perch height and perch diameter is more in plantation and average canopy cover is more in shola. More diverse perch surface is available and used in shola compared to plantation. The average body temperature is high in plantation compared to shola and the body temperature is directly proportional to atmospheric temperature and substrate temperature. There is no significant difference in Flight Initiation Distance (FID) between shola and plantation. FID is inversely correlated to substrate temperature.