Diversity, Distribution and Status of Bats on the Andaman and Nicobar Islands, India
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Diversity, distribution and status of bats on the Andaman and Nicobar Islands, India B ANDANA A UL, P.J.J. BATES,D.L.HARRISON and G . M ARIMUTHU Abstract Information on the bat fauna of the Andaman Introduction and Nicobar Islands was limited previously to the results of sporadic surveys, with no specific focus on the habitats or lthough the Andaman and Nicobar Islands are distribution of the species. We carried out the first extensive Apolitically a part of the Indian subcontinent, they ffi survey of the Andaman and Nicobar Islands during have biogeographical a nities with Sumatra and the 1988 1999 2003–2006, covering 40 islands. Our objective was to map Lesser Sundas (Rodgers & Panwar, ; Das, ). The the bat species, their habitats and distribution. This resulted mammalian fauna of these islands comprises a rich 1902 1967 in identification of 25 bat species representing 13 genera, assemblage of rodents and bats (Miller, ; Hill, ; 1975 1980 1990 location of . 300 roosts and validation of previously Nath & Chatervedi, ; Saha, ; Das, ; Pande 1991 13 5 357 recorded species. Notable findings included the rediscovery et al., ); % of the , recorded animal species are 1984 of the endemic Nicobar flying fox Pteropus faunulus after endemic (Rao, ). This excludes the marine mammals, a century and its extinction from the type locality on Car none of which are endemic. Endemism is pronounced in 39 270 1971 Nicobar Island, the sighting of an albino Hipposideros % of the species and subspecies of birds (Das, ; 1974 55 58 32 diadema nicobarensis from Katchal Island, and the first Abdulali, ), % of the mammal species, %of 83 20 10 records of Rhinolophus yunanensis, Murina cyclotis and the reptile species and % of the amphibian species 1985 2002 Hipposideros larvatus from the Andaman Islands, and (Rao & DevRoy, ; Andrews & Sankaran, ). Taphozous melanopogon, Murina cyclotis, Pipistrellus spp., Common terrestrial mammals include the Andaman wild Myotis horsfieldii dryas and Cynopterus brachyotis from pig Sus scrofa andamanensis, crab eating macaque Macaca the Nicobar Islands. Threats to the bat fauna appear to fascicularis umbrosa, Andaman masked palm civet Paguma be primarily roost disturbance and hunting for sport. larvata tytlerii, Andaman spiny shrew Crocidura andama- Anthropogenic pressure on species of Pteropus is high as nensis, Nicobar tree shrew Tupaia nicobarica nicobarica, hunting occurs throughout the year. Secondary sources Andaman horse-shoe bat Rhinolophus cognatus and and our field observations confirmed the decline of Pteropus lesser short-nosed bat Cynopterus brachyotis. Introduced in several islands as a result of hunting and alteration to mammals include the spotted deer Axis axis (now occurring habitats. We introduced a community initiative to monitor throughout South, Middle and North Andaman Islands), and protect roosts and foraging sites close to settlements in goats Capra sp. (on Barren and Narcondum Islands) the Nicobar Islands. Priorities identified for conservation of and elephant Elephas maximus (on Interview Island). the bat fauna of the archipelagos are mitigation of threats to Bats are sensitive to habitat disturbance and land- 1993 flying foxes and cave dwelling bats, initiation of research on scape changes from anthropogenic activities (Zubaid, ; 2008 endemic bat species such as P. faunulus, and a voluntary ban Struebig et al., ) and could be used as indicator species. 1 by local communities on hunting in specific areas and seasons. Previous records (Supplementary Table S ) of bat species in the Andaman and Nicobar Islands are the result of Keywords Andaman and Nicobar Islands, bats, com- faunal exploration and collection of species (Hill, 1967, 1971; munity initiative, local extinction, new records, Pteropus Abdulali, 1976a,b; Rao et al., 1994; Das, 1998, 1999; Deb, faunulus 1998). Miller (1902) listed 12 bat species and other small mammals, and provided the first description of the endemic This paper contains supplementary material that can be fruit bat Pteropus faunulus, from Car Nicobar Island. found online at http://journals.cambridge.org Bates & Harrison (1997) compiled a list of 23 species from museum specimens and records (e.g. Miller, 1902; Hill, 1967). BANDANA AUL (Corresponding author) Department of Animal Behaviour & Here we report the first extensive survey of the bats of Physiology, Madurai Kamraj University, Madurai 6250421, India. E-mail the Andaman and Nicobar Islands and the threats to bandana_aul@rediffmail.com these species from hunting and disturbance in their day P.J.J. BATES and D.L. HARRISON Harrison Zoological Museum, Centre of Systematics and Biodiversity Research, Sevenoaks, Kent, UK roosts. We focused on identifying the distribution of species across the islands, validating past records and mapping G. MARIMUTHU Department of Animal Behaviour & Physiology, School of Biological Sciences, Madurai Kamaraj University, Madurai, Tamil Nadu, India roosts. We also attempted to initiate community partici- Received 26 December 2011. Revision requested 27 February 2012. pation in conservation of bats by proposing a voluntary Accepted 8 May 2012. First published online 21 February 2014. hunting ban and adoption of roosts close to settlements © 2014 Fauna & Flora International, Oryx, 48(2), 204–212 doi:10.1017/S0030605312000646 Downloaded from https://www.cambridge.org/core. IP address: 170.106.202.8, on 02 Oct 2021 at 13:50:34, subject to the Cambridge Core terms of use, available at https://www.cambridge.org/core/terms. https://doi.org/10.1017/S0030605312000646 Bats of the Andaman and Nicobar Islands 205 on inhabited islands. This is especially applicable in the mango and guava. These plantations are not for commercial Nicobar Islands where the wildlife laws favour the purposes and are mostly to supplement the diet of people indigenous communities, who have been granted special in the settlements. Nets were also deployed in primary hunting rights under Section 56 of the Indian Wildlife forests and secondary forest with and without streams. (Protection) Act, 1972 (Anon, 1994). In a pilot radio-tracking Unique habitats such as freshwater swamps and fringing study we successfully tracked 11 P. faunulus, locating a day forest habitats with grasslands, mangroves and littoral roost and the foraging range. forests were also sampled. These unique habitats are restricted in extent. For example, Little Andaman Island is Study area the only island with freshwater swamps, and grasslands are restricted to the Central Nicobar Group. All bats The Andaman and Nicobar Islands (Figs 1 & 2) lie in the Bay captured were kept in cloth bags and released at point of of Bengal between India and Myanmar, parallel to the coast capture after data collection. Data collected included length of Myanmar. The Andaman Islands are separated from the of fore arm, sex, weight and pelage colour. In accordance Nicobar Islands by the Ten Degree Channel. Both the island with internationally accepted procedures (Kunz, 2009), nets groups have a tropical climate throughout the year, over streams were set at a height to ensure the last shelf was with temperatures of 18–34 °C, a mean annual rainfall of well above the water, to avoid drowning of captured 3,000–3,500 mm, and relative humidity of 75–95%. The individuals. forest can be broadly classified as tropical evergreen. Net nights were calculated by multiplying the number of Grasslands are unique to the Central Nicobar Group nets deployed by the number of nights of sampling at (Pande et al., 1991). The topography of the islands is hilly each site. Capture success for each species, by island, was and undulating; maximum altitudes are 732 m at Saddle calculated as the total number of individuals of a species Peak on North Andaman Island and 568 m at Mt Thullier captured on an island divided by the total number of on Great Nicobar Island (Southern Nicobar Group; individuals of all species combined captured on the island, Oldham, 1885). Among the total of 306 islands in the multiplied by 100. Species richness of a site is the total archipelagos 33 are inhabited and 94 are designated as number of bat species recorded. Sanctuaries, including two islands in the Andaman Islands Day roosts were identified from earlier records that are tribal reserves. The entire Nicobar Islands are under (Sankaran, 1998) through informal discussions with in- the provisions of the Andaman and Nicobar Protection of habitants, and searches of potential sites. At each roost the Aboriginal Tribes Regulation of 1956 and entry to them is species present and the roost type were recorded. Population restricted to Indian nationals. sizes were estimated by counting the individuals of each species. Methods Caves surveyed were within the forest and at the seashore. Caves within forest were cracks in the rocks, in Surveys of the large islands and representative samples undulating terrain, below the ground and on inland hills, of small islands were carried out on 26 islands (39 sites) where they occurred as clefts or cracks under a rocky hill, in the Andaman Islands and 14 islands (20 sites) in the forming large cave complexes. There are such complexes Nicobar Islands (Figs 1 & 2) during 2003–2006. We made at Cliff Bay Sanctuary (41 caves) in the North Andaman an additional survey after the occurrence of the tsunami Group, and Interview Island (34 caves) and Baratang Island that resulted from the Sumatra–Andaman earthquake of (190 inland forest caves, including some small caves) in 26 December 2004, to record any damage to cave roosts and the Middle Andaman Group. We did not locate any cave roosts of Pteropus melanotus, particularly in the mangrove complexes in the Nicobar Islands. Where entry by adults forest belts. Secondary data on hunting, and locations and to caves was not possible mist nets on entrances were used to shift of roosts were regularly obtained from locally trained ascertain the presence or absence of bats. Upon identifica- individuals during 2008–2011. tion of roosts we attempted to explore all accessible areas, Standard ground-level mist nets were deployed between record the species present in each cave and count the 17.00 and 02.00, monitored every 30 minutes, for 121 and approximate numbers in each roost.