Journal of Threatened Taxa | www.threatenedtaxa.org | 26
December 2019 | 11(15): 14955–14970
A review
on status of mammals in Meghalaya, India
Adrian Wansaindor
Lyngdoh 1, Honnavalli
Nagaraj Kumara 2, P.V. Karunakaran
3 & Santhanakrishnan Babu
4
1,2,3,4 Salim Ali Centre for Ornithology and Natural History, Anaikatty Post, Coimbatore, Tamil Nadu 641108, India.
1 adrian.lyngdoh@gmail.com,
2 honnavallik@gmail.com (corresponding author), 3 karunakaran.pv@gmail.com,
4 sanbabs@gmail.com
Abstract: In this paper we present an updated checklist of
mammals found in Meghalaya. Using online
databases and search engines for available literature, we provide the
scientific names, accepted English names, conservation status as per IUCN Red
List, Indian Wildlife (Protection) Act schedules, appendices in CITES, local
distribution status, endemism, last reported sighting, an account of previous
studies carried out relative to mammals and a tentative bibliography of the
mammalian species found in Meghalaya. A
total of 162 species were found to be existing in the state with Chiropterans
forming the largest group and 27 species found to be threatened, seven Near
Threatened and seven Data Deficient.
Keywords: Checklist, CITES, Indian Wildlife (Protection) Act,
IUCN, mammalian species, northeastern India.
Abbreviation: BBL—Balpakram Baghmara Landscape; CEPF—Critical Ecosystem Partnership
Fund; CITES—Convention on International Trade in Endangered Species of Wild
Fauna and Flora (Appendix I, II and III); EGH—East Garo Hills; EJH—East Jaintia Hills; EKH—East Khasi Hills; GBIF—Global
Biodiversity Information Facility; GH—Garo Hills; ISFR—Indian State Forest
Report; IUCN—International Union for Conservation of Nature; IUCN Red List of
Threatened Species: Categories (CR—Critically Endangered; EN—Endangered;
VU—Vulnerable; NT—Near Threatened; LC—Least Concern; NA—Not Assessed);
IWPA—Indian Wildlife (Protection) Act, 1972 (Schedule I, II, III, IV, and V);
JH—Jaintia Hills; KH—Khasi Hills; MBSAP—The Meghalaya
State Biodiversity Strategy and Action Plan; NP—National Park; RB—Ri-Bhoi; RF—Reserved Forest; SGH—South Garo Hills; WGH—West
Garo Hills; WJH—West Jaintia Hills; WKH—West Khasi
Hills; WS—Wildlife Sanctuary; WWF—World Wide Fund for Nature; ZSI—Zoological
Survey of India.
doi: https://doi.org/10.11609/jott.5192.11.15.14955-14970
|
ZooBank: urn:lsid:zoobank.org:pub:CD7F14D9-F322-44D3-85D6-6273EF22D40D
Editor: L.A.K. Singh, Bhubaneswar,
Odisha, India. Date of publication: 26 December 2019
(online & print)
Manuscript details: #5192 | Received 26 June 2019 |
Final received 30 November 2019 | Finally accepted 05 December 2019
Citation: Lyngdoh, A.W., H.N. Kumara,
P.V. Karunakaran & S. Babu
(2019). A review on status of mammals in
Meghalaya, India. Journal of Threatened Taxa 11(15): 14955–14970. https://doi.org/10.11609/jott.5192.11.15.14955-14970
Copyright: © Lyngdoh et al. 2019. Creative Commons Attribution
4.0 International License. JoTT allows unrestricted use, reproduction, and
distribution of this article in any medium by adequate credit to the author(s)
and the source of publication.
Funding: Implemented by the Ministry of Environment, Forest & Climate Change (MoEF&CC), Nodal and Serving hub with G.B. Pant National Institute of Himalayan Environment
& Sustainable Development (GBPNI/NMHS-2017-18/MG
32, dated: 28.03.2018).
Competing interests: The authors declare no competing
interests.
Author details: Adrian W. Lingdoh was a research biologist in the
project which was exploring the biodiversity and its importance in the
community conservation reserves of Meghalaya. Now he is an independent
researcher studying Slow Loris and its conservation in Meghalaya. Honnavalli N. Kumara is a Principal Scientist in SACON. His
research focuses on various aspects of conservation. P.V. Karunakaran is a Principal
Scientist in SACON. His research focuses on vegetation science and landscape
ecology. Santhanakrishnan Babu is
Senior Scientist at Sálim Ali Centre for Ornithology
and Natural History (SACON), Tamil Nadu. His research focuses on ornithology,
landscape ecology, and Remote Sensing & GIS.
Author contribution: Conceptualization: Honnavalli Nagaraj Kumara. Data compilation: Adrian W Lyngdoh. Manuscript writing: Adrian W Lyngdoh
and Honnavalli Nagaraj Kumara. Mentoring, supervision, and editing: Honnavalli Nagaraj Kumara, P. V. Karunakaran and Santhanakrishnan Babu
Acknowledgements: This communication is part of a project on the characterization and
assessment of Conservation Values of Community Reserves in Meghalaya. We are thankful to the National Mission on
Himalayan Studies (NMHS) under the Ministry of Environment, Forest and Climate
Change, Government of India for funding this study (GBPNI/NMHS-2017-18/MG 32,
dated: 28 March 2018). Dr. Kireet Kumar, Scientist and
Nodal Officer and his team of scientists and other staff at the Project
Management Unit (PMU-NMHS), at the GB Pant National Institute of Himalayan
Environment and Sustainable Development (GBPNIHESD) are acknowledged for their
logistic support and timely actions for the smooth conduct of the project. Our sincere thanks are due to Shri H.C.
Chaudhary IFS, Additional Principal Chief Conservator of Forests (Wildlife)
& Chief Wildlife Warden (CWLW), Government of Meghalaya, and his
subordinate officers of the Forest and Environment Department, Government of
Meghalaya for facilitating to get the permission from the Community Reserve
Management Committee of Khasi, Garo and Jaintia Hills
for carrying out the study. We are
indebted to the Management Committees of each of the Community Reserves
who gave us permission for this work. At SACON, we thank Dr.
K. Sankar, Director, for his constant encouragement
and the support he extended to this project since its inception.
INTRODUCTION
The global mammalian fauna is represented by 6,495
species, of which 6,399 are extant and 96 are extinct (Mammal Diversity
Database 2019). India has a total of 423
species, which accounts for 7.81% of the global mammalian species (Sharma et
al. 2015). A majority of these species
are distributed in the four biodiversity hotspots of India—the Western Ghats
and Sri Lanka, the Himalaya, Indo-Burma, and Sundalands
biodiversity hotspots (Myers et al. 2000; CEPF 2016). The state of Meghalaya (25–26oN,
89.5–93oE; Figure 1) is part of the Indo-Burma biodiversity hotspot
along with other parts of northeastern India south of
the Brahmaputra River. This hotspot also includes parts of Bangladesh, Myanmar,
Thailand, Vietnam, Cambodia, Laos PDR, southern China and touches a small
portion of peninsular Malaysia and extends over two million square kilometers (Myers et al. 2000; Mittermeier et al.
2004). The Indo-Burma biodiversity
hotspot has been considered to be one of the most important regions in the
world and is ranked among the top 10 hotspots for irreplaceability due to high
species diversity and endemism (Myers et al. 2000; Mittermeier et al.
2004). Its forests, freshwater and
coastal ecosystems not only support many globally threatened species but also
the region’s human population. It houses
about 430 mammalian species of which 73 species are endemic to the
hotspot. Its natural habitat has been
reduced to about 5% of its original extent due to human activities such as
shifting cultivation, conversion to farmland, plantations, logging, deliberate
forest fires, mining, damming and poaching (Tordoff et al. 2012). This has earned the hotspot a rank in the top
five for most threatened (Mittermeier et al. 2004; Tordoff et al. 2012).
Meghalaya, nestled in the northeastern
India biogeographic zone is a conflux of the Indo-Malayan and Indo-Chinese
biogeographic realms (Palni et al. 2011) and as such
is considered one of the richest habitats of Asia with a high diversity of
mammals, birds, and plants (Rodgers & Panwar 1988, as cited in WWF
2019). Its diverse landscapes with
gentle slopes in the north, steep slopes in the south forming deep valleys and
a central plateau (Mani 1974; MBSAP 2017) has resulted in a diversification of
its forests and wildlife. About 76.45%
of its total geographic area is under forest cover (ISFR 2017) and is composed
of tropical evergreen forests, tropical semi-evergreen forests, tropical moist
and deciduous forests, grasslands and savanna, temperate forests and
subtropical pine forests (Haridasan & Rao
1985). Meghalaya is also a part of the
Meghalaya subtropical forests ecoregion and has been described as the gateway
to the Malayan fauna and as such houses closely related species with different
distributional ranges such as the Indian and Chinese pangolins (WWF 2019). In recognition of its important position of
harbouring diverse mammalian species, we attempt to update the list of
mammalian species found in the region.
One of the earliest accounts of mammals in the state
of Meghalaya dates back to the 19th century surveys that covered
British India and other neighbouring regions (Harlan & Burrough
1834; McClelland 1841; Blyth 1852; Dobson 1874; Jerdon
1874; Sterndale 1884; Blanford--
-1888–91). Between 1847 and 1875,
numerous collectors had also visited the region and documented the mammals
found in the state (Alfred 1995). During
the early decades of the 20th century, many mammalian specimens were
collected from various parts of the state and a description of some of the
species was done (Allen 1906; Kemp 1924; Hinton & Lindsay 1926). From the second half of the century, the
Zoological Survey of India (ZSI) has also published numerous works on the fauna
of the state (Alfred 1995). Apart from
the work done by ZSI, other authors have also compiled lists of mammals found
in Meghalaya as part of a wider effort to document mammals of the entire Indian
subcontinent (Pocock 1939, 1941; Ellerman & Morrison-Scott 1951; Ellerman
1961; Prater 1965; Corbett & Hill 1992).
Between 1989–94, ZSI conducted a systematic survey of
all fauna in the state including mammals through specimens available in its
repository and secondary literature, and published a checklist of mammals (Das
et al. 1995). A total of 139 mammal species
were reported, representing 83 genera and 27 families in the state. This list, however, had also erroneously
cited species that were not historically found in the region. Since then, many mammalian species have been
discovered and an updated checklist is warranted. Recently, Choudhury (2013)
compiled a comprehensive checklist and systematic review of all mammals found
in northeastern India including Meghalaya based on
primary as well as secondary sources, which serves as an important source of
information for the mammals of northeastern India. Kakati and Kabra (2015) reported 51 mammalian species in Balpakram-Baghmara Landscape, Garo Hills, while Goswami (2015) documented 20 mammalian species in Jaintia Hills.
Meghalaya’s extensive karst topography provided the ideal settings for
the diversification of bats with a tentative list of about 65 bat species
having been reported from the state (Saikia et al.
2018). Considering all the new additions
to the state in recent years by surveys
and records from all available literature, we provide an updated checklist of
mammals for Meghalaya along with their distribution, conservation and
management status.
METHODS
We collected all published and gray
literature available about the mammals of Meghalaya and thoroughly reviewed
them to prepare a comprehensive list of mammals that have been reported to
occur in Meghalaya. Online databases,
web portals, websites and sites such as Google Scholar, ResearchGate,
Biodiversity Heritage Library, Shodhganga, GBIF, and
IUCN Red List were accessed for collecting the literature. Technical Reports and unpublished literature
were also collected from the authors through personal communication. Conservation status as per IUCN Red List, schedule
category in Indian Wildlife (Protection) Act 1972 (IWPA), Appendices in
Convention on International Trade in Endangered Species of Wild Fauna and Flora
(CITES) and last reported sighting in the state were compiled to highlight the
importance of the landscape for mammal conservation (Image 1). The taxonomic arrangement of the species
follows Wilson & Reeder (2005) and Wilson & Mittermeier (2009).
RESULTS AND DISCUSSION
A total of 162 species of mammals belonging to 31
families were reported from the state of Meghalaya (Table 1; Figure 2). Chiropterans formed the largest group of
mammals with 65 species (40%). This was
followed by rodents with 35 (22%) and carnivores with 34 species (22%). The rest of the groups constituted less than
20% of the total mammal diversity in the state (Figure 3). Evening bats formed the largest group at 35
species, followed by murids at 21, sciurid and mustelids at 10 each. Among the 162 species, 27 are threatened (one
Critically Endangered, nine Endangered, 17 Vulnerable) and seven species each
as Near Threatened and Data Deficient (Figure 2, Table 2). None of the species, however, are endemic to
Meghalaya.
Mammals excluded from the Meghalaya list
A few species have been excluded from this list
because they could be locally extinct, erroneously mentioned in the literature
or have not been formally recognized as a separate species. A description of their past and current
distribution in northeastern India is also summarized
here in support of their exclusion from this list.
Barasingha Rucervus duvaucelii was stated to be present in East Khasi Hills
of Meghalaya (Das et al. 1995) although no record of its existence is available
except for a hunting report in 1894 on three Barasinghas
shot on the border of East Garo Hills of Meghalaya and Goalpara
District of Assam (Choudhury 2001; Choudhury 2013). In northeastern
India, the species’ past range extended along the foothills of the Himalaya
from upper Assam and were common in the Brahmaputra Valley with many having
still existed in a few districts of Assam till as late as 1934 (Blanford 1888–91; Lydekker 1915; Bhadian 1934; Schaller 1967). Since then, however, their numbers have
drastically dwindled and their current distribution in northeastern
India is now restricted to only a few pockets of Assam in Kaziranga
NP and Manas NP (Schaller 1967; Choudhury 2001a; Srinivasulu et al. 2012; IUCN 2019).
Chital Axis
axis was stated to be present in Ri-Bhoi and East Khasi Hills districts of Meghalaya (Das et
al. 1995). It is, however, unlikely to
have occurred as there is no historical record of the species occurring south
of the Brahmaputra River (Choudhury 2001a).
In northeastern India, Chital is restricted to
the western part of Assam, north of the Brahmaputra River (Choudhury 2001a;
IUCN 2019) with its most recent record at Manas NP
(Bhatt et al. 2018). Its easternmost
record was at Dhunsiri River in Darrang
District reported in 1935 by A.J.W. Milroy (De 1935).
Chousingha Tetracerus quadricornis was reported to be present in West Garo
Hills although it could be a misidentified Naemorhedus
goral (Das et al. 1995). This
species is endemic to peninsular India and parts of lowland Nepal (Leslie et
al. 2009; Srinivasulu et al. 2012; IUCN 2019).
Himalayan Serow Capricornis thar in this paper is reported as Capricornis
rubidus.
Due to the lack of information on the taxonomic status of the Capricornis sp. in northeastern
India, some reports have considered them as C. thar
(Srinivasulu et al. 2012; IUCN 2019) although others
have reported it as C. rubidus (Choudhury
2013; Kakati et al. 2015).
Indian Crested Porcupine Hystrix indica was reported from Meghalaya (Goswami
2015); however, this species is not distributed in northeastern
India (IUCN 2019).
Dormer’s Bat Scotozous dormeri was reported by Sinha (1995) based on a damaged
male specimen from Shillong but examination of its
teeth and external characteristics suggested it to be of another species, Hypsugo cadornae (Saikia et al. 2018).
Dusky Leaf-nosed Bat Hipposideros ater reported in Meghalaya from a single record that is
doubtful, and is excluded from this list (Kurup 1968;
Choudhury 2013; Saikia et al. 2018).
A new species of bat, Hipposideros
khasiana was reported in Meghalaya based on the
differences in call frequencies of the bats from their closely related species H.
larvatus (Thabah et al.
2006). Due to the lack of type material,
however, this species has not yet been formally recognized as a distinct
species from H. larvatus (Saikia
2018; Saikia et al. 2018).
Specimens collected from Siju
Cave in Meghalaya and identified as the Eastern Bent-winged Bat (Miniopterus fuliginosus)
(Sinha 1999) were found to be that of M. magnater
(Saikia et al. 2018). M. fuliginosus although
likely to be found in the state is yet to be formally identified (Saikia et al. 2018).
A note on natural history of other species
Elephants: Numerous
studies on Asian Elephants Elephas maximus have been carried out in
Meghalaya (Johnsingh 1996a,b; Choudhury 1999, 2004,
2007; Johnsingh & Williams 1999; Williams & Johnsingh 2004; Datta-Roy et al.
2008, 2009; Marak 2009; Kaul et al. 2010; Marcot et al. 2011; Goswami et
al. 2014). Meghalaya is known to
have one of the largest and densest populations of Elephants in India with a
population of 1,811 as per 2008 records (Datta-Roy et
al. 2008; Marcot 2011). The State Forest Department conducted the
first Elephant census in and around Balpakram National
Park (NP) in 1981. The number of
Elephants was estimated to be 2,333 (Gogoi &
Choudhury, as cited in Williams & Johnsingh
1996a). The first state-wide Elephant
census was conducted in 1993 which estimated Elephants to be numbering 1,850
(William & Johnsingh 1996a; Choudhury 1999). The number increased slightly to 1,868
Elephants in 2002 (Marcot 2011). Fourteen distinct populations of Elephants
were identified throughout northeastern India
(Choudhury 1999). Two of the populations
are shared between Assam and Meghalaya.
These two populations form a sizeable portion of the estimated 11,000
Elephants found in northeastern India (>
50%). One large population was found in
Ri-Bhoi and Jaintia Hills
districts and another in West Khasi Hills, Ri-Bhoi,
and Garo Hills districts. Populations in
western Khasi Hills are around more than 800 and in Garo Hills around 1,800,
with the latter having a density of 0.74 km-2. A smaller population of Elephants exist in
some parts of Jaintia Hills (Choudhury 1999). Areas in and around Nokrek
NP and Balpakram-Baghmara Landscape in Garo Hills
have been reported to have the highest potential for long term conservation of
Elephants in the region (William & Johnsingh
1996a) and as such warrant greater conservation efforts. Three critical Elephant corridors were
identified in Garo Hills, one of them faced tremendous anthropogenic pressure
and another one was at risk of being overexploited for timber and coal as most
of the corridor is private or community owned land and does not come under the
control of the Forest Department (William & Johnsingh
1996b). In 2003, six corridors (five in
Garo Hills and one in Jaintia Hills) were identified
by the Wildlife Trust of India for the long-term conservation of Elephants in
the state (Kaul et al. 2010).
Human-Elephant interaction is intense in some parts of
Garo Hills. This is mainly attributed to
disturbances caused by ‘jhum’ (slash and burn regime) and coal mining (William
& Johnsingh 1996a). Retaliatory killing due to crops being raided
and poaching of Elephants has also increased over the years (Johnsingh & William 2004). The presence of Elephants in human-occupied
areas and intensity of conflicts with humans varies highly across the
landscape. Various factors such as sowing
and harvesting season of crops and availability of wild forage had an influence
on the Elephant visits (Datta-Roy et al. 2008, 2009);
however, in most cases, these Elephant visits were not negative in nature. Elephants have also been observed to use
sites close to PAs more intensely than sites away from the PAs. The presence of humans further augmented this
trend (Goswami et al. 2014). A few Elephants (40–50) from South Garo Hills
have been reported to cross the border annually to Bangladesh and lone males in
Jaintia Hills have also been observed to cross the
International boundary occasionally (Choudhury 2007).
Primates: The distribution and status of different primate
species were mapped, and the forest status and human pressures in northeastern India were assessed by Srivastava (2006). Extensive surveys were carried out throughout
the region between 1994 and 1999. The
survey reported the presence of Rhesus Macaque Macaca
mulatta, Assamese Macaque Macaca
assamensis, Northern Pig-Tailed Macaque Macaca leonina,
Stump-Tailed Macaque Macaca arctoides, Capped Langur Trachypithecus
pileatus, Western Hoolock Gibbon Hoolock hoolock, and Bengal Slow Loris Nycticebus
bengalensis in Meghalaya. All the species were
observed to occur in very low densities.
Habitat loss and hunting were reported to be the main threats to the
primates. In some cases, indiscriminate
hunting had extirpated local populations despite the availability of large
tracts of primary forest. Interactions
with humans due to crop raiding have led to retaliatory killing of macaques and
langurs (Srivastava 2006).
Stump-Tailed Macaque was reported to occur in Mawsynram area of the Khasi Hills, Balpakram
NP and Nokrek RF while Pig-Tailed Macaque were
reported in all districts including Mawsynram area of
East Khasi Hills, West Garo Hills, and West Khasi Hills (Biswas 1977; Sati
& Alfred 1990; Molur et al. 2003). Rhesus Macaque was reported to occur in Garo
and Khasi hills, Assamese Macaque in Balpakram NP, Songsek Tasek RF and Siju WS, and Capped Langur in Garo Hills (Molur et al. 2003).
Habitat destruction and hunting were stated to be the main threats for
all the species.
Preliminary investigations have reported the
occurrence of the Bengal Slow Loris in Meghalaya (Radhakrishna et al. 2006;
Nandini et al. 2009; Radhakrishna et al. 2010).
The species occurs in very low numbers and its population may have
reduced over the years owing to threats such as forest fragmentation, vehicle
collision, and hunting (Radhakrishna et al. 2006). Other major threats to the species were
hunting for bushmeat, capture for pets, man-made fires, mining and conversion
of forests to plantations (Radhakrishna et al. 2010). The species has been sighted in Nongkhyllem WS, Narpuh RF, Baghmara RF, Balpakram NP, and Nokrek NP although its density is very low (Molur et al. 2003; Kakati et al.
2009; Radhakrishna et al. 2010).
The occurrence of Western Hoolock Gibbons has been
reported in East Garo Hills, South Garo Hills, Ri-Bhoi,
and Khasi Hill districts (Baskaran 1975; Molur et al.
2003). Hoolock Gibbon also occurs in 32
localities in West Garo Hills (Alfred & Sati 1990). Hoolock Gibbon populations in West Garo Hills
had declined between 2007 and 1985–87 by 26.2% owing to human disturbances such
as tree felling, jhum, livestock grazing, and poaching (Alfred &
Sati 1990; Sati 2011). It was observed
that the rate of survival might have been severely affected and establishment
of new colonies was not happening.
Rodents: Rodents have
hardly been studied in Meghalaya, except for a couple of studies that reported
on the partial albinism of White-Bellied Rat Rattus niviventer
(Rajagopal & Mandal 1965). A
faunal account of all rodent species found in India was provided through an
extensive collection available at the British Museum (Ellerman 1961). Accounts of all mammalian species including a
few rodent species found in the Khasi, Jaintia, and
Garo hills region was also provided by Hinton & Lindsay (1926).
Chiropterans: Bats have
been well documented in Meghalaya. About
65 species have been reported in the state (Saikia et
al. 2018). One of the first scientific
records of bats in Meghalaya was of the description of Scotomanes
ornatus done by Blyth in 1851 (Saikia et al. 2018).
Since then bats have been documented throughout the Khasi, Jaintia, and Garo hills (Dobson 1871, 1872, 1874; Thomas
1921; Kemp 1924; Hinton & Lindsay 1926; Topal
1970; Lal 1977; Sinha 1990, 1994, 1995, 1999; Thabah
& Bates 2002; Thabah et al. 2006, 2007; Ruedi et al. 2012a,b, 2014; Thong et al. 2017; Saikia et al. 2017, 2018; Korad
2018). Most of the studies reported only
the taxonomic status and distribution of the bat species. One of the few studies that focused on the
ecology of bats (Thabah et al. 2007) reported on the
feeding and echolocation behavior of the Great
Evening Bat Ia io. The authors found that the species preyed on
birds, although coleopterans formed the main constituent of their diet.
Unregulated mining activities for limestone and coal
near cave systems pose a threat to the caves and the fauna they harbour (Saikia 2018).
Expansion of plantations, demand for firewood and deforestation
associated with mining activities threaten the survival of bat species as well
as all other forest-dwelling species (Ruedi et al.
2012a, 2014). Hunting of bats for a
supplementary source of protein is another threat. Improvised techniques are employed for their
capture from caves by locals, and the number of captured bats has been reported
to go as high as 100 on a single night.
Some of the bat meat is sold in local markets (Ruedi
et al. 2012b; Saikia et al. 2018). This overharvesting has led to a decline in
the bat population, with some colonies retreating to inaccessible cliffs and
caverns (Saikia et al. 2018).
Dhole: A questionnaire-based survey reported that Dhole Cuon alpinus was
still common in Garo Hills although throughout the state it had become very
rare (Johnsingh 1985). The species was last sighted in Garo Hills (Kakati & Kabra 2015).
Bears: A few studies have reported the occurrence of three
bear species in Meghalaya, viz., Asian Black Bear Ursus
thibetanus, Sloth Bear Melursus
ursinus, and Malayan Sun Bear Helarctus
malayanus (Blanford
1888–91; Hinton & Lindsay 1926; Sathyakumar 2001;
Johnsingh 2003; Sathyakumar
& Choudhury 2007; Choudhury 2011; Kakati & Kabra 2015). An
Asian Black Bear was photo-captured in Balpakram-Baghmara
Landscape in Garo Hills (Kakati & Kabra 2015). The
occurrence of Sloth Bear in Meghalaya was confirmed through a specimen acquired
from Khasi Hills and preserved at the Zoological Survey of India as well as by
local hunters who were familiar with all three species (Choudhury 2011). Choudhury (2011) also reported the sighting
of a Malayan Sun Bear pelt from Balpakram NP in the
early 1980s; however, no systematic study has been carried out till date for
any of the bear species.
The major threats faced by these species are habitat
loss, construction of linear infrastructure and dams, coal mining and
shortening of jhum cultivation cycles (Sathyakumar
2001; Choudhury 2011). Asiatic Black
Bear also faces pressure from poaching for its bile (Choudhury 2011).
Mustelids: Specimens of
Yellow-bellied Weasel Mustela kathiah and skins of Burmese Ferret-badger Melogale personata
were acquired from Khasi and Jaintia hills (Pillai
& Biswas 1971). The authors stated
that the Khasis ascribed magical properties to the teeth of the weasel and used
it to remove fish bone stuck in the throat.
The Burmese Ferret-badger and Small-toothed Palm Civet Arctogalida trivirgata
were camera-trapped for the first time by Kakati et
al. (2014a, 2014b) in Garo Hills. The
Burmese Ferret-badger had earlier only been recorded in Khasi Hills (Choudhury
2013).
Red Panda: A disjunct
population of Red Panda Ailurus fulgens, locally known as Matchibel,
was reported in Meghalaya through four skins of the species collected from Nokrek and Balpakram in Garo
Hills in the 1960s and 1980s (Choudhury 1997, 2000a,b). The largest known specimen was shot in the
early 1960s in Nokrek NP (Choudhury 2000a). This was the first record of the species in a
tropical forest. It also holds the
record for the lowest elevation reported for the species at 200m. This population was thought to have migrated
through the Patkai and Naga ranges to the Garo
Hills. It was also stated to be found in
the Khasi Hills (Choudhury 2000b) although no evidence was provided.
Ungulates: Populations
of Wild Water Buffalo Bubalus arnee- have declined in Meghalaya as well as in the
whole of northeastern India owing to the destruction
of habitat through the conversion of elephant-grass jungles to farmland,
hunting pressure and transmission of diseases by livestock. In Meghalaya, there currently exists only a
small population in Balpakram NP (Choudhury 1994).
The Gaur Bos gaurus
is mainly found in South Garo Hills and West Khasi Hills although a small
population is also found in Ri-Bhoi District
(Choudhury 2002).
CONCLUSION
Meghalaya being part of the Indo-Burma Biodiversity
Hotspot and also hosting a diverse array of Indo-Malayan species is an
important landscape for the conservation of many of the mammalian species that
exist in the subcontinent. With about
38% of all Indian mammals found in the state, it is worthwhile to emphasize the
need for greater conservation efforts in this region. Although a decent number of studies have been
conducted, most have focused only on Asian Elephants and only in the Garo Hills
region while hardly a handful of studies have focused their attention on other
species and in other parts of the state; most of the studies on other species
have been limited to preliminary investigations and provide only a synoptic
view of species distribution, occurrences and threats. Certain taxa such as the chiropterans have in
recent years been well documented, but are restricted only to the taxonomic
field. Other taxa such as the rodents,
although representing the second largest group in the state, have hardly been
studied. A wider concerted effort in
conducting additional studies on other lesser appreciated groups and lesser
known species and tackling both ecological as well as human-wildlife questions
would provide a firm foundation for undertaking holistic conservation actions
to ensure the persistence of the mammalian fauna in the state.
Table 1. Checklist of mammals found in Meghalaya,
India.
|
Taxa |
Common
name |
IUCN
Red List status |
Wildlife
Protection Act, 1972 schedule/ status |
CITES |
Distribution |
Source |
|
Order
Proboscidea: Elephants |
|
|
|
|
||
|
Family
Elephantidae: Elephants |
|
|
|
|
||
1 |
Elephas
maximus |
Asian
Elephant |
EN |
Sch I
(Part I) |
I |
WGH, EGH,
SGH, RB, WKH, JH |
1,2,3,4,5 |
|
Order
Scandentia: Tree Shrews |
|
|
|
|
||
|
Family
Tupaiidae: Tree Shrew |
|
|
|
|
||
2 |
Tupaia belangeri |
Common Tree
Shrew |
LC |
Sch II
(Part I) |
II |
WGH, EGH,
EKH |
1,2,3,4 |
|
Order
Primates: Primates |
|
|
|
|
|
|
|
Family
Lorisidae: Lorises |
|
|
|
|
||
3 |
Nycticebus bengalensis |
Bengal Slow
Loris |
VU |
Sch I
(Part I) |
I |
WGH, EGH,
EKH |
1,2,3,4 |
|
Family
Cercopithecidae: Old World Monkeys |
|
|
|
|||
4 |
Macaca arctoides |
Stump-tailed
Macaque |
VU |
Sch II
(Part I) |
II |
All
districts |
1,2,3,4 |
5 |
Macaca assamensis |
Assamese
Macaque |
VU |
Sch II
(Part I) |
II |
All
districts |
1,2,3,4 |
6 |
Macaca leonina |
Northern
Pig-Tailed Macaque |
VU |
Sch II
(Part I) |
II |
All
districts |
1,2,3,4 |
7 |
Macaca mulatta |
Rhesus
Macaque |
LC |
Sch II
(Part I) |
II |
All
districts |
1,2,3,4,5 |
8 |
Trachypithecus pileatus |
Capped
Langur |
VU |
Sch I
(Part I) |
I |
All
districts |
1,2,3,4,5 |
|
Family
Hylobatidae: Gibbons |
|
|
|
|
|
|
9 |
Hoolock
hoolock |
Western
Hoolock Gibbon |
EN |
Sch I
(Part I) |
I |
WGH, EGH,
SGH, RB, WKH |
1,2,3,4,5 |
|
Order
Rodentia: Rodents |
|
|||||
|
Family
Muridae: Rats and Mice |
|
|
|
|||
10 |
Bandicota bengalensis |
Lesser
Bandicoot Rat |
LC |
Sch V |
NA |
EKH, JH, GH |
1,2,3 |
11 |
Bandicota indica |
Large
Bandicoot Rat |
LC |
Sch V |
NA |
EKH, JH, GH |
1,2,3 |
12 |
Berylmys bowersi |
Bower's Rat |
LC |
Sch V |
NA |
Mawphlang |
1,3,9 |
13 |
Berylmys mackenziei |
Kenneth's
White-toothed Rat |
DD |
Sch V |
NA |
Shillong |
1,2,3 |
14 |
Chiropodomys gliroides |
Pencil-tailed
Tree Rat |
LC |
Sch V |
NA |
EKH, JH |
1,2,3 |
15 |
Leopoldamys edwardsi |
Long-tailed
Giant Rat |
LC |
Sch V |
NA |
WGH, EGH,
RB, JH |
1,2,3 |
16 |
Micromys minutus |
Harvest
Mouse |
LC |
Sch V |
NA |
EKH |
1,2,3 |
17 |
Mus
booduga |
Little
Indian Field Mouse |
LC |
Sch V |
NA |
WGH, EGH,
EKH, JH |
1,2,3 |
18 |
Mus
cervicolor |
Fawn-coloured
Mouse |
LC |
Sch V |
NA |
EKH, GH, JH |
1,2,3 |
19 |
Mus
cookii |
Cooke's
Mouse |
LC |
Sch V |
NA |
Khonshnon, Shangpung |
1,3,9 |
20 |
Mus
musculus |
House Mouse |
LC |
Sch V |
NA |
All
districts |
1,2,3 |
21 |
Mus
pahari |
Sikkim
Mouse |
LC |
Sch V |
NA |
WGH, EKH,
JH |
1,2,3 |
22 |
Niviventer fulvescens |
Chestnut
Rat |
LC |
Sch V |
NA |
WGH, EKH,
RB, JH |
1,2,3 |
23 |
Niviventer confucianus |
Chinese
White-bellied Rat |
LC |
Sch V |
NA |
WGH, EKH,
RB, JH |
3 |
24 |
Niviventer niviventer |
White-bellied
Rat |
LC |
Sch IV |
NA |
EKH, RB, JH |
1,2,3,4 |
25 |
Rattus
andamanensis |
Indo-Chinese
Forest Rat |
LC |
Sch V |
NA |
WGH, EKH,
RB, JH |
1,3,9 |
26 |
Rattus
nitidus |
White-footed
Himalayan Rat |
LC |
Sch V |
NA |
WGH, EGH,
SGH, EKH, RB, JB |
1,2,3 |
27 |
Rattus
rattus |
House Rat |
LC |
Sch V |
NA |
All
districts |
1,2,3 |
28 |
Rattus
norvegicus |
Brown Rat |
LC |
Sch V |
NA |
EKH |
2,3 |
29 |
Rattus
tanezumi |
Oriental
House Rat |
LC |
Sch V |
NA |
All
districts |
1,3 |
30 |
Vandeleuria
oleracea |
Indian
Long-tailed Tree Mouse |
LC |
Sch V |
NA |
EKH, JH |
1,2,3 |
|
Family
Sciuridae: Squirrels |
|
|
|
|
|
|
31 |
Ratufa bicolor |
Malayan
Giant Squirrel |
NT |
Sch II
(Part I) |
II |
All
districts |
1,2,3,4,5 |
32 |
Belomys pearsonii |
Hairy-footed
Flying Squirrel |
DD |
Sch II
(Part I) |
NA |
GH |
2,3 |
33 |
Hylopetes alboniger |
Parti-coloured
Flying Squirrel |
LC |
Sch II
(Part I) |
NA |
EKH, JH |
1,2,3 |
34 |
Petaurista petaurista |
Red Giant
Flying Squirrel |
LC |
Sch II
(Part I) |
NA |
All
districts |
1,2,3 |
35 |
Petaurista philippensis |
Indian
Giant Flying Squirrel |
LC |
Sch II
(Part I) |
NA |
GH, KH |
1,2,3 |
36 |
Callosciurus erythraeus |
Red-bellied
Squirrel |
LC |
No mention
of this in WPA |
NA |
All
districts |
2,3,4 |
37 |
Callosciurus pygerythrus |
Hoary-bellied
Squirrel |
LC |
Sch II
(Part I) |
NA |
All
districts |
1,2,3,4,5 |
38 |
Dremomys lokriah |
Orange-bellied
Himalayan Squirrel |
LC |
Sch II
(Part I) |
NA |
All
districts |
1,2,3 |
39 |
Funambulus pennanti |
Himalayan
Five-striped Palm Squirrel |
LC |
Sch IV |
NA |
KH, JH |
2,3 |
40 |
Tamiops macclellandii |
Himalayan
Striped Squirrel |
LC |
No mention
of this in WPA |
NA |
EKH |
1,2,3,4 |
|
Family
Spalacidae: Bomboo Rats |
|
|
|
|
|
|
41 |
Cannomys badius |
Bay Bamboo
Rat |
LC |
Sch V |
NA |
EGH, EKH,
JH |
1,2,3 |
42 |
Rhizomys pruinosus |
Hoary
Bamboo Rat |
LC |
Sch V |
NA |
All
districts |
1,2,3 |
|
Family
Hystricidae: Old-World Porcupines |
|
|
|
|||
43 |
Atherurus macrourus |
Asiatic
Brush-Tailed Porcupine |
LC |
Sch II
(Part I) |
NA |
All
districts |
1,2,3,4 |
44 |
Hystrix brachyura |
Himalayan
Crestless Porcupine |
LC |
Sch II
(Part I) |
NA |
All
districts |
1,2,3,4,5 |
|
Order
Lagomorpha: Hares and Rabbits |
|
|
|
|
||
|
Family
Leporidae: Hares |
|
|
|
|
|
|
45 |
Caprolagus hispidus |
Hispid Hare |
EN |
Sch I
(Part I) |
I |
Balpakram NP
and Chenggni border SGH |
3 |
46 |
Lepus
nigricollis |
Indian Hare |
LC |
Sch IV |
NA |
All
districts |
1,2,3,4 |
|
Order
Eulipotyphla: Moles and Shrews |
|
|
|
|
||
|
Family
Soricidae: Shrews |
|
|
|
|
|
|
47 |
Crocidura fuliginosa |
Southeast
Asian Shrew |
LC |
NA |
NA |
WGH, EKH |
2,3 |
48 |
Crocidura attenuata |
Asian Grey
Shrew |
LC |
NA |
NA |
WGH, EKH,
JH |
1,2,3 |
49 |
Suncus etruscus nudipes |
Pygmy
White-toothed Shrew |
LC |
NA |
NA |
EKH, JH |
1,2,3 |
50 |
Suncus murinus |
Asian House
Shrew |
LC |
NA |
NA |
EKH, WGH,
JH |
1,2,3 |
51 |
Anourosorex assamensis |
Assam Mole
Shrew |
LC |
NA |
NA |
EKH, JH |
1,2,3 |
|
Family
Talpidae: Moles |
|
|
|
|
|
|
52 |
Euroscaptor micrura |
Indian
Short-tailed Mole |
LC |
NA |
NA |
EKH, JH, GH |
1,2,3 |
53 |
Parascaptor leucura |
White-tailed
Mole |
LC |
NA |
NA |
EKH, JH |
1,2,3 |
|
Order
Chiroptera: Bats |
|
|
|
|
|
|
|
Family
Miniopteridae: Long-fingered Bats |
|
|
|
|
||
54 |
Miniopterus pusillus |
Lesser
Bent-winged Bat |
LC |
No mention
of this in WPA |
NA |
Umlyngsha,
EJH |
7 |
55 |
Miniopterus |
Large
Bent-winged Bat |
LC |
No mention
of this in WPA |
NA |
SGH, EJH,
EKH, WKH, RB. |
7 |
|
Family
Pteropodidae: Old World Fruit Bats |
|
|
|
|||
56 |
Cynopterus brachyotis |
Lesser
Short-nosed Fruit Bat |
LC |
Sch V |
NA |
EJH, WGH |
1,3,7 |
57 |
Cynopterus
sphinx |
Greater
Short-nosed Fruit Bat |
LC |
Sch V |
NA |
WGH, EGH,
SGH, KH, EJH |
1,2,3,7 |
58 |
Eonycteris spelaea |
Lesser Dawn
Bat |
LC |
Sch IV
|
NA |
SGH, EKH,
JH |
1,2,3,7 |
59 |
Macroglossus sobrinus |
Hill
Long-tongued Fruit Bat |
LC |
Sch IV
|
NA |
EKH, JH |
1,2,3,7 |
60 |
Megaerops niphanae |
Northern
Tailless |
LC |
Sch V |
NA |
WKH, EJH |
1,2,3,7 |
61 |
Pteropus giganteus |
Indian
Flying Fox |
LC |
Sch V |
II |
EKH, RB,
WGH |
1,2,3,4,7 |
62 |
Rousettus
leschenaultii |
Leschenault's Rousette |
LC |
No mention
of this in WPA |
NA |
WGH, EGH,
SGH, EKH, JH |
1,2,3,7 |
|
Family
Rhinolophidae: Horseshoe Bats |
|
|
|
|||
63 |
Rhinolophus
affinis |
Intermediate
Horseshoe Bat |
LC |
NA |
NA |
EKH, JH |
1,2,3,7 |
64 |
Rhinolophus
lepidus |
Blyth's
Horseshoe Bat |
LC |
NA |
NA |
KH, JH, SGH |
1,2,3,7 |
65 |
Rhinolophus luctus |
Great
Woolly Horseshoe Bat |
LC |
NA |
NA |
KH, JH |
1,2,3,7 |
66 |
Rhinolophus macrotis |
Big-eared
Horseshoe Bat |
LC |
NA |
NA |
KH, EJH |
1,3,7 |
67 |
Rhinolophus
pearsonii |
Pearson's Horsehsoe Bat |
LC |
NA |
NA |
KH, JH, GH |
1,2,3,7 |
68 |
Rhinolophus
pusillus |
Least
Horseshoe Bat |
LC |
NA |
NA |
EKH, SGH,
WGH, JH |
1,2,3,7 |
69 |
Rhinolophus
siamensis |
Thai
Horseshoe Bat |
LC |
NA |
NA |
EJH |
7 |
70 |
Rhinolophus
sinicus |
Chinese
Horseshoe Bat |
LC |
NA |
NA |
EKH, EJH |
7 |
71 |
Rhinolophus
subbadius |
Little
Nepalese Horseshoe Bat |
LC |
NA |
NA |
GH, EKH |
1,2,3,7 |
|
Family
Hipposideridae: Old-World Leaf-Nosed Bats |
|
|
|
|||
72 |
Coelops frithii |
Tailless
Leaf-nosed Bat |
LC |
NA |
NA |
KH |
1,2,3,7 |
73 |
Hipposideros
armiger |
Great
Himalayan Leaf-nosed Bat |
LC |
NA |
NA |
KH, JH, GH |
1,2,3,7 |
74 |
Hipposideros cineraceus |
Least
Leaf-nosed Bat |
LC |
NA |
NA |
EKH, JH, RB |
1,2,3,7 |
75 |
Hipposideros larvatus |
Horsfield's
Leaf-nosed Bat |
LC |
NA |
NA |
WGH, KH,
EJH, RB |
1,2,3,7 |
76 |
Hipposideros pomona |
Anderson's
Leaf-nosed Bat |
LC |
NA |
NA |
SGH, EKH,
RB, EJH |
1,2,3,7 |
77 |
Hipposideros |
Indian
Leaf-nosed Bat |
LC |
NA |
NA |
EKH, RB,
EJH, SGH |
2,3,7 |
|
Family
Megadermatidae: False Vampire Bats |
|
|
|
|||
78 |
Megaderma
lyra |
Greater
False Vampire |
LC |
NA |
NA |
WGH, RB,
EKH, EJH |
1,2,3,7 |
79 |
Megaderma spasma |
Lesser
False Vampire |
LC |
NA |
NA |
BBL, RB,
EKH |
1,3,4,7 |
|
Family
Emballonuridae: Sheathtail
Bats |
|
|
|
|
||
80 |
Saccolaimus saccolaimus |
Bare-rumped |
LC |
NA |
NA |
Phulbari,
WGH |
1,3,7 |
81 |
Taphozous melanopogon |
Black-bearded
Tomb Bat |
LC |
NA |
NA |
WKH |
1,7 |
|
Family
Molossidae: Free-Tailed Bats |
|
|
|
|
||
82 |
Chaerephon plicatus |
Wrinkle-lipped
Free-tailed Bat |
LC |
NA |
NA |
EKH, WGH |
1,2,3,7 |
83 |
Otomops wroughtoni |
Wroughton's
Free-tailed Bat |
DD |
Sch I
(Part I) |
NA |
EKH, JH |
1,3,7 |
|
Family
Vespertilionidae: Evening Bats |
|
|
|
|
||
84 |
Arielulus circumdatus |
Black-gilded
Pipistrelle |
LC |
NA |
NA |
EKH |
1,2,3,7 |
85 |
Eptesicus pachyotis |
Thick-eared
Bat |
LC |
NA |
NA |
KH |
1,2,3,7 |
86 |
Scotomanes ornatus |
Harlequin
Bat |
LC |
NA |
NA |
EGH, EKH,
JH |
1,2,3,7 |
87 |
Scotophilus heathii |
Asiatic
Greater Yellow House Bat |
LC |
NA |
NA |
WGH, EKH |
1,2,3,7 |
88 |
Scotophilus kuhlii |
Lesser
Asiatic Yellow House Bat |
LC |
NA |
NA |
GH, EKH |
1,2,3,7 |
89 |
Pipistrellus ceylonicus* |
Kelaart's
Pipistrelle |
LC |
NA |
NA |
EJK |
1,7 |
90 |
Pipistrellus coromandra |
Indian
Pipistrelle |
LC |
NA |
NA |
JH, EKH,
RB, GH |
1,2,3,7 |
91 |
Pipistrellus javanicus |
Javan
Pipistrelle |
LC |
NA |
NA |
KH |
1,7 |
92 |
Pipistrellus paterculus |
Mount Popa Pipistrelle |
LC |
NA |
NA |
EJH |
1,7 |
93 |
Pipistrellus mimus |
Least
Pipistrelle |
LC |
NA |
NA |
WGH, EKH |
1,2,3,7 |
94 |
Pipistrellus |
Kuhl's
Pipistrelle |
LC |
NA |
NA |
EKH |
3,7 |
95 |
Barbastella leucomelas |
Eastern
Barbastelle |
LC |
NA |
NA |
JH, KH |
1,2,3,7 |
96 |
Plecotus homochrous |
Long-eared
Bat |
LC |
NA |
NA |
KH |
1,2,7 |
97 |
Hypsugo joffrei |
Joffre's
Pipistrelle |
DD |
NA |
NA |
EKH |
7 |
98 |
Hypsugo savii |
Savi's
Pipistrelle |
LC |
NA |
NA |
EKH |
1,2,3,7 |
99 |
Ia io |
Great
Evening Bat |
LC |
NA |
NA |
KH, EJH |
1,2,3,7 |
100 |
Tylonycteris malayana |
Greater
Bamboo Bat |
LC |
NA |
NA |
EJH |
7 |
101 |
Tylonycteris pachypus |
Lesser
Bamboo Bat |
LC |
NA |
NA |
WGH, EKH |
1,2,3,7 |
102 |
Myotis
altarium |
Szechwan |
LC |
NA |
NA |
EKH, EJH |
7 |
103 |
Myotis
formosus |
Hodgson's
Bat |
LC |
NA |
NA |
EKH |
1,2,3,7 |
104 |
Myotis
horsfieldii |
Horsfield's
Myotis |
LC |
NA |
NA |
JH |
1,2,3,7 |
105 |
Myotis
laniger |
Chinese
Water Myotis |
LC |
NA |
NA |
EKH |
1,2,3,7 |
106 |
Myotis
longipes |
Kashmir
Cave Bat |
DD |
NA |
NA |
SGH, EJH,
EKH, WKH |
1,2,3,7 |
107 |
Myotis
muricola |
Nepalese
Whiskered Bat |
LC |
NA |
NA |
WJH, EKH |
1,3,7 |
108 |
Myotis
pilosus |
Rickett’s |
NT |
NA |
NA |
EKH |
7 |
109 |
Myotis
siligorensis |
Himalayan |
LC |
NA |
NA |
JH, KH |
1,2,3,7 |
110 |
Harpiocephalus harpia |
Lesser
Hairy-winged Bat |
LC |
NA |
NA |
EKH |
1,2,3,7 |
111 |
Murina aurata |
Little
Tube-nosed Bat |
LC |
NA |
NA |
EKH |
1,3,7 |
112 |
Murina cyclotis |
Round-eared
Tube-nosed Bat |
LC |
NA |
NA |
EKH, JH |
1,2,3,7 |
113 |
Murina huttoni |
Hutton’s |
LC |
NA |
NA |
EKH, EJH |
3,7 |
114 |
Murina jaintiana |
Jaintia
Tube-Nosed |
DD |
NA |
NA |
EKH, EJH |
7 |
115 |
Murina pluvialis |
Rainy
Forest |
DD |
NA |
NA |
EKH, EJH |
7 |
116 |
Murina tubinaris |
Scully's
Tube-nosed Bat |
LC |
NA |
NA |
JH, EKH |
1,2,3,7 |
117 |
Kerivoula hardwickii |
Common
Woolly Bat |
LC |
NA |
NA |
SGH, WJH |
1,2,3,7 |
118 |
Kerivoula |
Kachin
Woolly |
LC |
NA |
NA |
EKH, EJH |
7 |
|
Order
Pholidota: Pangolins |
|
|
|
|
|
|
|
Family
Manidae: Pangolins |
|
|
|
|
|
|
119 |
Manis
crassicaudata |
Indian
Pangolin |
EN |
Sch I
(Part I) |
I |
WGH, EGH,
SGH |
1,
2, 3 |
120 |
Manis
pentadactyla |
Chinese
Pangolin |
CR |
Sch I
(Part I) |
I |
SGH, EKH |
1,2,3,5 |
|
Order
Carnivora: Carnivores |
|
|
|
|
|
|
|
Family
Felidae: Cats |
|
|
|
|
|
|
121 |
Catopuma temminckii |
Asian
Golden Cat |
NT |
Sch I
(Part I) |
I |
EGH, SGH,
JH |
1,2,3,8 |
122 |
Felis chaus |
Jungle Cat |
LC |
Sch II
(Part I) |
II |
WGH, EGH,
SGH |
1,2,3,8 |
123 |
Pardofelis
marmorata |
Marbled Cat |
NT |
Sch I
(Part I) |
I |
GH |
1,2,3,4 |
124 |
Prionailurus bengalensis |
Leopard Cat |
LC |
Sch I
(Part I) |
I/II |
All
districts |
1,2,3,4 |
125 |
Prionailurus viverrinus |
Fishing Cat |
VU |
Sch I
(Part I) |
II |
All
districts |
1,3 |
126 |
Neofelis nebulosa |
Clouded
Leopard |
VU |
Sch I
(Part I) |
I |
All
districts |
1,2,3,4 |
127 |
Panthera pardus |
Leopard |
VU |
Sch I
(Part I) |
I |
All
districts |
1,2,3,4,5 |
128 |
Panthera tigris |
Tiger |
EN |
Sch I
(Part I) |
I |
All
districts |
1,2,3,6 |
|
Family
Viverridae: Civets |
|
|
|
|
|
|
129 |
Arctictis
binturong |
Binturong |
VU |
Sch I
(Part I) |
III |
All
districts |
1,2,3 |
130 |
Arctogalidia trivirgata |
Small-toothed
Palm Civet |
LC |
Sch II
(Part I) |
NA |
BBL |
1,3,4 |
131 |
Paguma larvata |
Himalayan
Palm Civet |
LC |
Sch II
(Part I) |
III |
All
districts |
1,2,3,4 |
132 |
Paradoxurus hermaphroditus |
Common Palm
Civet |
LC |
Sch II
(Part I) |
III |
All
districts |
1,2,3,4 |
133 |
Viverra zibetha |
Large
Indian Civet |
LC |
Sch II
(Part I) |
III |
All
districts |
1,2,3,4 |
134 |
Viverricula indica |
Small
Indian Civet |
LC |
Sch II
(Part I) |
III |
WGH |
1,2,3,4 |
|
Family
Herpestidae: Mongooses |
|
|
|
|
|
|
135 |
Herpestes javanicus |
Small
Indian Mongoose |
LC |
Sch II
(Part I) |
III |
All
districts |
1,2,3,4 |
136 |
Herpestes edwardsii |
Indian Grey
Mongoose |
LC |
Sch II
(Part I) |
III |
WGH |
1,2,3 |
137 |
Herpestes urva |
Crab-eating
Mongoose |
LC |
Sch II
(Part I) |
III |
WGH, EGH |
1,2,3,4,5 |
|
Family
Canidae: Dogs and Foxes |
|
|
|
|
|
|
138 |
Canis
aureus |
Golden
Jackal |
LC |
Sch II
(Part I) |
III |
WGH, EGH,
SGH, JH |
1,2,3,4 |
139 |
Cuon alpinus |
Wild Dog |
EN |
Sch II
(Part I) |
II |
All
districts |
1,2,3,4 |
140 |
Vulpes
bengalensis |
Indian Fox |
LC |
Sch II
(Part I) |
III |
SGH |
1,2,3 |
|
Family
Ursidae: Bears |
|
|
|
|
|
|
141 |
Helarctos malayanus |
Malayan Sun
Bear |
VU |
Sch I
(Part I) |
I |
All
districts |
1,2,3 |
142 |
Melursus ursinus |
Sloth Bear |
VU |
Sch II
(Part I) |
I |
RB, EKH, GH |
1,2,3 |
143 |
Ursus thibetanus |
Asiatic
Black Bear |
VU |
Sch II
(Part I) |
I |
All
districts |
1,2,3,4 |
|
Family
Mustelidae: Weasels, Badgers, and Otters |
|
|
|
|||
144 |
Aonyx cinerea |
Asian
Small-clawed Otter |
VU |
Sch I
(Part I) |
II |
WGH, JH |
1,2,3 |
145 |
Lutra lutra |
Common
Otter |
NT |
Sch II
(Part I) |
I |
All
districts |
2,3 |
146 |
Lutrogale perspicillata |
Smooth-coated
Otter |
VU |
Sch II
(Part I) |
II |
WGH |
1,2,3,4 |
147 |
Arctonyx albogularis |
Northern
Hog Badger |
LC |
Sch I
(Part I) |
NA |
All
districts |
1 |
148 |
Arctonyx collaris |
Hog Badger |
VU |
Sch I
(Part I) |
NA |
All
districts |
1,2,3,4 |
149 |
Martes flavigula |
Yellow-throated
Marten |
LC |
Sch II
(Part I) |
III |
All
districts |
1,2,3,4 |
150 |
Melogale moschata |
Small-toothed
Ferret Badger |
LC |
Sch II
(Part I) |
NA |
KH |
1,2,3,4 |
151 |
Melogale personata |
Burmese
Ferret-badger |
LC |
Sch II
(Part I) |
NA |
BBL, KH |
1,2,3,4 |
152 |
Mustela kathiah |
Yellow-bellied
Weasel |
LC |
Sch II
(Part I) |
III |
WKH, EKH |
1,2,3 |
153 |
Mustela strigidorsa |
Stripe-backed
Weasel |
LC |
NA |
NA |
EKH, JH |
1,3 |
|
Family
Ailuridae: Red Panda |
|
|
|
|
|
|
154 |
Ailurus fulgens |
Red Panda |
EN |
Sch I
(Part I) |
I |
WGH, EGH,
SGH, WKH, EKH |
1,2,3 |
|
Order
Artiodactyla: Even-Toed Ungulates |
|
|
|
|
||
|
Family
Suidae: Pigs |
|
|
|
|
|
|
155 |
Sus
scrofa |
Indian Wild
Boar |
LC |
Sch
III |
NA |
All
districts |
1,2,3,4,5 |
|
Family
Cervidae: Deer |
|
|
|
|
||
156 |
Muntiacus
vaginalis |
Indian
Muntjac |
LC |
Sch
III |
NA |
All
districts |
1,2,3,4,5 |
157 |
Axis
porcinus |
Hog Deer |
EN |
Sch
III |
I/III |
RB, GH |
2,3 |
158 |
Rusa
unicolor |
Sambar |
VU |
Sch
III |
NA |
WGH, EGH,
SGH, RB, EKH |
1,2,3,4 |
|
Family
Bovidae: Cattle, Antelopes, and Goats |
|
|
|
|
||
159 |
Bubalus arnee |
Wild Water
Buffalo |
EN |
Sch I
(Part I) |
III |
BBL, Siju WS, WKH |
2,3 |
160 |
Bos
gaurus |
Gaur |
VU |
Sch I
(Part I) |
I |
All
districts |
1,2,3,4 |
161 |
Capricornis rubidus |
Red Serow |
NT |
Sch I
(Part I) |
I |
All
districts |
3,4 |
162 |
Naemorhedus
griseus |
Chinese
Goral |
NT |
Sch
III |
I |
WGH |
1,2,3 |
Sources: 1—IUCN Red List | 2—Das et al. (1995) |
3—Choudhury (2013) | 4—Kakati & Kabra (2015) | 5—Goswami (2015) |
6—Kumar et al. (2010) | 7—Saikia et al. (2018) |
8—Mukherjee et al. (2019) | 9—Molur et al.
(2005). EGH—East Garo Hills | EJH—East Jaintia Hills | EKH—East Khasi Hills | GH—Garo Hills | JH—Jaintia Hills | KH—Khasi Hills | RB—Ri-Bhoi
| RF—Reserved Forest | SGH—South Garo Hills | WGH—West Garo Hills | WJH—West Jaintia Hills | WKH—West Khasi Hills.
Table 2. Conservation status
according to IUCN Red List, IWPA 1972 and CITES. Numbers show the number of
species.
Indian Wildlife (Protection) Act, 1972 |
|
Schedule I |
23 |
Schedule II |
33 |
Schedule III |
5 |
Schedule IV |
9 |
Schedule V |
23 |
Not assessed |
65 |
CITES (2017) |
|
Appendix I |
22 |
Appendix II |
12 |
Appendix III |
13 |
For
figures & image -- click here
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