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    Mitigation measures for doubling of the Tiniaghat-Castlerock-Caronzol, SWR Railway track, Karnataka
    (Wildlife Institute of India, Dehradun, 2020) WII
    The Indian Railway network, spread across 1,23,542 km (as of 2018-2019), is a vital component of transportation infrastructure since its inception in 1850. The railways have been pivotal in integrating markets, increasing trade, shaping finances besides serving as the backbone of linear transportation services. Even though railways are regarded to be an environmentally friendly option when compared to other forms of linear infrastructure, the development and expansion of rail networks pose challenges to the environment and biodiversity of the forest areas it passes through. Railways can pose both physical and behavioral barriers to wildlife and have negative impacts such as disturbance and mortality on populations living in proximity. The Railway Vikas Nigam Limited (RVNL) has proposed the doubling of the existing railway track between Hospet, Tinaighat, and Vasco Port that measures 345 km in length. The sanctioned project consists of 2 main phases: doubling of a line between Hospet and Tinaighat (Phase I) and between Tinaighat and Vasco (Phase II). At present, the existing single line limits the capacity of running trains in the critical ghat (hilly) section. Given the terrain of the region, landslides during the monsoons interfere with the functioning of the line. RVNL has justified the doubling of the railway track by stating that in addition to improving mobility and all-weather rail links in the region, the proposed doubling would also increase connectivity, trade, and commerce, enhance tourist flow, augment intermediate railway station facilities, and reduce bottlenecks of railway traffic in the ghat section. The Western Ghats that extend along the south-western parts of India, is known to harbour a wide diversity of flora and fauna and is one of the four biodiversity hotspots of the Indian subcontinent. In terms of faunal diversity, the area is home to about 30% of Asian elephant population, about 33% of India's wild tiger population and about 26% of India's leopard population (Jhala et aI., 2019; Jhala et aI., 2020). The landscape forms one of the largest and most contiguous protected area networks in the country. Within the Western Ghats, the Anshi-Dandeli-Sharavathi Valley complex consists of the protected areas of Mollem-Netravali, Anshi-Dandeli, Sharavathi Valley-Mookambika along with reserved forests of Goa which continue to the Sahyadri Tiger Reserve in Maharashtra. The major tiger source population in the complex is that of the Anshi National Park and Dandeli WLS (Qureshi et aI., 2014) that together form the Kali Tiger Reserve. Among the important tiger source populations in the landscape is the Anshi and Dandeli tiger population that provides a critical link to the northern Western Ghats, extending up to Goa and South Maharashtra (Sahyadris), which is threatened by anthropogenic activities such as land-use conversion and construction of linear infrastructure. The landscape is also home to 252 species of amphibians with 90% endemics, 108 species of reptiles with 56% endemics (Dahanukar & Molur, 2020; srinivasulu et al. 2015), and about 600 species of evergreen woody plants with more than 60% endemic. In the past decade, more than 100 species of amphibians and -50 species of reptiles have been discovered from Western Ghats (Aengles et aI. , 2018; Dahanukar & Molur, 2020; reptiledatabase.org). The area where the railway doubling is proposed falls in the Uttara Kannada region of the northern Western Ghats which is known to harbor approximately 50 species of amphibians that constitute almost one-fourth of the total Western Ghats amphibian diversity (Ramachandra et aI., 2012). The approved alignment of the proposed line is parallel to the existing railway line and mostly lies within the railway land. However, the new railway (i)line is deemed to pass through the Kali (formerly Anshi-Dandeli) Tiger Reserve in the Uttar Kannada district of Karnataka and would impact the ecosystem during the construction and operational phase. Considering the irreplaceable ecological importance of the landscape and the critical link it provides for the Western Ghats, the project was required to obtain environmental clearance that included an environmental impact assessment study and a mitigation plan to reduce, offset and mitigate the negative impacts of the proposed doubling. A biodiversity assessment for the proposed line was then conducted by the Indian Institute of Science (IISc) during the years 2017-2020. Environmental and Biodiversity Assessment by IISc Two environmental assessment reports were submitted by IISc (Sukumar and Sitharam, 2017 and Suresh et aI., 2020), detailing the floral and faunal studies of the project area in two stretches of the proposed railway track (Kulem to Castlerock, and Castle rock to Tinaighat). The authors carried out detailed assessments on the vegetation of the area during both study periods, and the structu ral and functional aspects of vegetation, and forecasts of a loss of vegetation in alternative rail alignment scenarios were reported. For mammals, sign surveys, camera trapping, and opportunistic sightings were recorded to assess the presence of mammals near the railway track and to identify areas of high animal activity and movement. As a result, stretches of railway tracks specified by chainages and critical animal crossing zones were reported. General recommendations for mitigation were proposed for such areas. For the herpetofaunal component, the studies documented the diversity and rail kills of amphibians and reptiles in and around the study area. However, no specific mitigation measures were provided aimed at reducing the impacts on amphibians and reptiles. The Wildlife Institute of India (WII) was subsequently requested to undertake the task of proposing mitigation measures for the proposed railway track doubling project by the DIG (Wildlife), Ministry of Environment, Forest and Climate Change, Government of India vide Letter F. No. 6-55/2020WL(part) dated 28th August, 2020 recommending that "detailed study for prescribing mitigation measures in this difficult terrain may be conducted by Wildlife Institute of India, Dehradun. The study may cover the entire 25 km stretch of the project area from Castlerock in the Kamataka side to Kulem in Goa. The objective of the study by WII was to assess the length of existing and proposed railway track to suggest site-specific mitigation measures that will reduce the barrier effect, (ii) allow permeability for wildlife movement across the railway, and minimize rail-induced mortality. We carried out a rapid survey from 19th November to 5th December 2020. The main aims of the exercise were: 1. To assess potential animal crossing zones along the existing and proposed railway track. 2. To carry out inventory of herpetofauna along the railway track, identify potential microhabitats along the track. 3. Coalesce information obtained from field survey with baseline data in IISc assessment reports (2017, 2020), and 4. Suggest site-specific mitigation measures based on the intensive track survey, information obtained from field study and IISc reports. To identify potential animal crossing zones, we carried out camera trapping and sign surveys along the railway tracks. We also used rail mortality data from the Karnataka forest department and any opportunistic sighting or sign encountered during the survey to identify such areas. Visual encounter surveys, opportunistic surveys, stratified plot sampling, and collection of opportunistic rail kill data to assess the herpetofaunal diversity and identify critical zones for mitigation. We also surveyed the entire length of the existing alignment accompanied by a railway engineer to assess the proposed rail alignment, and review the crossing and drainage structures proposed by the railways in terms of suitability for animal crossing. The scope of constructing additional mitigation structures based on topography, probability of animal movement and engineering constraints was discussed on field. Summary of results Camera trapping spanning 660 trap nights yielded 156 captures of 17 mammals species along the railway track. We recorded 203 animal signs through sign surveys of 175 habitat plots near the railway track. A total of 47 species of herpetofauna was recorded during the survey. This number is expected to be higher since the study was conducted within a short period during the non-breeding season. The study revealed that perennial and seasonal streams, and ephemeral water bodies were crucial habitats for herpetofauna. Camera trap data indicated that tunnels along the railway track are being used as natural passages by animals for their movement across the landscape. Hotspots of animal activity were visualized by overlapping all animal signs, sightings, photo-captures and mortality data using kernel density analysis on GIS-platform. These were then combined with the hotspots identified in the IISc reports, and potential multi-taxa animal crossing zones were thus delineated. Mitigation measures for the rai/way track Mitigation measures for the proposed railway track evolved through a multi-step simultaneous process. We first evaluated the existing and proposed drainage and crossing structures on field, assessed the possibility of making the structures more suitable for wildlife movement and constructing additional non-drainage crossing structures, and finally overlapped potential multi-taxa crossing zones to finalise the location and dimensions of the crossing structures.
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    Macroecology of terrestrial herpetofauna in Andaman and Nicobar Archipelago
    (Wildlife Institute of India, Dehradun, 2014) Harikrishnan, S.; Vasudevan, K.; Das, Abhijit; Choudhury, B.C.; Dutta, S.K.; Das, Indraneil
    The islands arc system of Andaman & Nicobar Islands situated in the Bay of Bengal is a major contributor to the overall high biodiversity figures of India. These islands are part of two global biodiversity hotspots and contain an impressive array of endemic flora and fauna. The herpetofauna of these islands have been the subject of explorations since the 19th century when European naturalists started natural history collections in these islands. However, our understanding of the terrestrial herpetofauna of these islands has been restricted to anecdotal observations, field records and taxonomic studies.. We conducted a four year survey of terrestrial herpetofauna in Andaman & Nicobar Islands. During this period 24 islands were surveyed for terrestrial herpetofauna. For the sake of completion, data from prior surveys and museum records were also compiled. We recorded 65 species of terrestrial reptiles and 17 species of amphibians from across the Andaman & Nicobar Islands. We present a presence absence matrix for all species recorded from various islands. As expected, the largest islands had the highest number of species and smaller islands within an island groups tended to have communities that were subsets of the larger island community. Several new records and some new species were discovered during our surveys. We found that the terrestrial herpetofauna in Andaman & Nicobar Islands occur in relatively high densities in undisturbed habitats, reaching as high as 3630 individuals per hectare in Little Andaman Island. Patterns in body size distributions were mostly right skewed, but inter taxa differences were observed in this. The shape of body size distribution did not change between Andaman Islands and Nicobar Islands. Distribution of body sizes within communities of co-existing species of frogs and lizards revealed a highly structured distribution, but not in the case of snakes. Species cooccurrence patterns showed inter taxa and inter island group differences. Differences in biogeographic and colonization histories of both groups of islands are suspected to be the reasons behind the observed species co-occurrence patterns. Abundance and geographic distribution patterns were less clearly defined for both frogs and lizards. We suspect that introduced species such as chital and Indian bullfrog might have adverse impacts on native herpetofauna in the Andaman & Nicobar Islands. We attempt a classification of island herpetofauna according to their vulnerability to extinction. We also assess the current conservation status according to the IUCN criteria and legal protection status according to WPA, 1972, and show that majority of species occurring in the Andaman & Nicobar Islands have not yet been assessed properly. We conclude this report by providing a checklist of the herpetofauna, other than turtles and crocodiles, of Andaman & Nicobar Islands.
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    Assessment of Ecological settings and biodiversity values of Papikonda National Park and Indira Sagar (Polavaram) Multipurpose project Impact zone in Andhra Pradesh for development of migratory measures
    (Wildlife Institute of India, Dehradun, 2014) Sivakumar, K.; Johnson, J.A,.; Gokulakkannan, N.; Ray, Paromita; Katlam, Gitanjali; Bagaria, Priyamvada
    The Indira Sagar (Polavaram Project) Multipurpose Project envisages the construction of a zoned earth-cum-rock fill dam with an impervious core across the Godavari River in Polavaram. This project also includes the construction of two canals, viz. the Right Main Canal, extending over a distance of 174 km, and the Left Canal, extending over a distance of 181.5 km. The Right Canal will connect the water-surplus Godavari River with the water-deficient Krishna River in Vijayawada and supply 80 tmcft (226 MCM) of water to Budameru in Vijayawada. The Left Canal is designed to provide water to 12 lakh acres in the northern coastal districts besides meeting the drinking water needs of the urban and rural areas around these. It will connect with the Yeleru canal to bring water for industries (Vizag steel plant) and a drinking water supply. It will also supply the northern coastal districts of Visakhapatnam, Vizianagaram and Srikakulam with irrigation water. Apart from boosting irrigation in the region, this project will also provide drinking water to 28 lakh people in 540 villages along the canals and generate around 960 MW of hydro-electricity. Despite these benefits, the project has come under scrutiny from various quarters, especially its adverse impacts on various ecosystems that are closely linked with the Godavari River. Further, an area of 3267 ha of land in Bhadrachalam (S), Bhadrachalam (N), Paloncha, Krishna, Eluru, Kakinada and Visakhapatnam forest divisions also needs to be diverted for submergence, construction of a power house, digging of canals, etc. In this context, as per the direction of the Ministry of Environment & Forests, Government of India, vide their letter no. 8-123/2005-FC dated 26/29th December 2008, Point No. 7(ii), the Wildlife Institute of India (WII) initiated a short term (18-month) study to assess the impact of the project on the wild flora and fauna and the habitat and subsequently suggest mitigatory measures for the same. The status and distribution of certain taxa such as mammals, birds, herpertofauna and fishes were assessed using various census techniques. These included the use of line transects and camera traps and sign surveys for mammals, point counts for birds, quadrat methods for herpetofauna, CPUE (Catch Per Unit Effort) and market surveys for fishes and circular plots for vegetation assessment. Further, GIS and remote sensing tools were used to assess the land cover and land use pattern and potential impact of the project at the landscape level.
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    A rapid assessment of herpetofaunal diversity in Manas-Bhutan transboundary landscape
    (Wildlife Institute of India, Dehradun, 2014) Das, A.; Sharma, P.; Harikrishnan, S.; Ghosh, S.; Nath, A.; Dhar, D.; Mondol, J.; Wangdi, Y.
    This report provides a rapid assessment of the herpetofaunal diversity at the World Heritage site Manas which acts as a transboundary complex for a variety of species. The survey was conducted between 16 June 2014-23 June 2014. In Manas National park (MNP), India we surveyed Mathanguri, Doimari, Kuribeel, Uchila, Lotajhar and Bansbari areas and in Royal Manas National Park (RMNP), Bhutan, we surveyed Manas range and Panbang area. We used visual encounter search; opportunistic search and pitfall method to document the diversity of herpetofaunal species. Habitats surveyed include semi-evergreen forest, moist mixed deciduous forest, grassland, wetland and marshy areas. From MNP, we recorded 17 species of amphibians belonging to 13 genera and five families. Record of Feihyla vittatus, Rhacophorus maximus, Rhabdophis himalayanus and Microhyla butleri are significant. From RMNP, we recorded 12 species of amphibians belonging to 10 genera. 31% of all the recorded species from RMNP constitute new report for Bhutan. Among amphibians, Uperodon globulosus and Ingerana borealis are a new addition to Bhutan fauna. Records of Calotes maria, Cnemaspis assamensis, Ptyctolaemus gularis, Varanus salvator from RMNP also adds to new records for Bhutan. Among the recorded species, Python bivittatus and Varanus bengalensis have been accorded the highest legal protection status, under Schedule I of the Indian Wildlife (Protection) Act, 1972. Naja naja, Ophiophagus hannah and Xenochrophis piscator are listed in Schedule II, while all the other snake species are under Schedule IV of the Act. Of the recorded species Varanua bengalensis, Melanochelys tricarinata are under Appendix I of CITES, Varanus salvator, Python bivittatus, Hardella thurjii, Melanochelys trijuga, Indotestudo elongata, Ophiophagus hannah, are listed in Appendix II of CITES. The only amphibian species Hoplobatrachus tigerinus is under CITES II and Xenochrophis piscator is under Appendix III of CITES.
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    Diversity and ecology of herpetofauna of Panna Tiger Reserve, Madhya Pradesh : Final Report
    (Wildlife Institute of India, Dehradun, 2019) Das, Abijit; Prasad, V.K.; Murthy, S.
    This study was conducted to know the status of herpetofauna even in the most protected areas such as Tiger Reserves and National Parks in India to protect the species from any local extinction. Hence, inventory and documentation of herpetofauna in protected areas becomes critical. In order to fill this lacuna, we executed systematic surveys using standard and integrated protocols to document the herpetofauna assemblage in Panna Tiger Reserve. The project was sanctioned for two years starting from 2017 to 2019 with two major seasons of monsoon, post monsoon, summers and winters) to collect data from the field. The objectives of the project are follows as:- To determine the species richness and diversity of herpetofauna in Panna Tiger Reserve. 2. To map and identify the distribution pattern of herpetofauna species with respect to their habitats and breeding sites. 3. To classify the herpetofauna community assemblage across various major habitats and to identify the species diversity, richness and evenness within the various major habitats in Panna Tiger Reserve landscape. 4. To discover and describe any potentially novel species in the region. 5. To obtain the information on species ecology and natural history. Describing ecological and behavioral interaction within species and describe novel characters which be used in species monitoring programmes. 6. To build capacity and create awareness and education amongst the various major stakeholders including forest department, officials, local villagers and students to promote conservation of herpetofauna.