Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 February 2023 | 15(2): 22567–22573
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.8082.15.2.22567-22573
#8082 | Received 30
June 2022 | Final received 11 January 2023 | Finally accepted 06 February 2023
On the occurrence of Eurasian
Otter Lutra lutra
(Carnivora: Mustelidae) in Neeru stream of Chenab catchment, Jammu & Kashmir,
India
Dinesh Singh 1, Anil Thakar 2 &
Neeraj Sharma 3
1–3 Institute of Mountain
Environment, Bhaderwah Campus, University of Jammu,
Union territory of Jammu & Kashmir 182222, India.
1 itzmed12@gmail.com, 2 anilenv0@gmail.com,
3 nirazsharma@gmail.com (corresponding author)
Abstract: This communication reports the
first photographic record of Eurasian Otter Lutra
lutra in a
hill stream in Jammu & Kashmir, putting an end to doubts over its presence
in the upper Chenab catchment. Three individuals were photographed during a
limited camera trap survey conducted in Neeru stream,
a left bank tributary of river Chenab during mid-October 2020. We argue that
rapid human population influx, infrastructure expansion, and pollution have
altered the hydro morphology of Neeru stream,
affecting the otter population. This observation calls for more intensive otter
surveys in the nearby smaller basins of Neeru, Kalnai, & Sewa and other
large tributaries of Chenab River, combining occupancy surveys with camera
traps for improved conservation and management of the species in the region.
Keywords: Camera trap, dense escape cover,
flagship species, hill stream, holts and dens, semi-aquatic mammal, retaliatory
killings, shore vegetation.
Editor: Honnavalli N. Kumara, Salim Ali
Centre for Ornithology and Natural History, Coimbatore, India. Date of publication: 26 February
2023 (online & print)
Citation: Singh, D., A. Thakar & N. Sharma (2023). On the occurrence of
Eurasian Otter Lutra lutra
(Carnivora: Mustelidae) in Neeru
stream of Chenab catchment, Jammu & Kashmir, India. Journal of Threatened Taxa 15(2): 22567–22573. https://doi.org/10.11609/jott.8082.15.2.22567-22573
Copyright: © Singh et al. 2023. Creative Commons Attribution
4.0 International License. JoTT allows unrestricted use, reproduction, and
distribution of this article in any medium by providing adequate credit to the
author(s) and the source of publication.
Funding: The surveys
were partly funded by Department
of Wildlife Protection, Govt.
of Jammu and Kashmir.
Competing interests: The authors
declare no competing interests.
Author details: Dr. Dinesh
Singh is a lecturer in the Faculty of Life Sciences, Institute
of Mountain Environment (IME), Bhaderwah
Campus, University of Jammu. He received
a doctorate for his work on ‘Ecological attributes and vegetation responses to environmental variables in upper Bhaderwah Valley, J&K’ in
2019. Aside from his
interest in alpine vegetation and
flora, he has contributed to
the exploration of other animal groups in the region, including
mammals, birds, odonata, and butterflies.
Mr. Anil Thakar is a junior research fellow in NMHS sponsored project on ‘Himalayan
alpine biodiversity characterization
and information system network’.
Dr. Neeraj Sharma is an assistant professor in the Faculty of Life Sciences in IME, Bhaderwah
Campus where he is actively
involved in research on high altitude
biodiversity, wildlife ecology, riparian ecology, avian ecology, and hill
stream dynamics, as well as scientific
outreach and extension on different facets
of mountain environment. Besides
investigating the externally aided projects on biodiversity
monitoring and assessment in the
region, he is actively engaged in guiding Ph.D students and
research interns.
Author contributions:
Dinesh Singh conducted the field surveys, camera trapping, data analysis and
drafted the manuscript; Anil Thakar helped
in camera trapping, data collection, analysis, and writing the
manuscript; Neeraj Sharma conceptualized, designed, and executed the
surveys, assisted first author in writing and editing the manuscript, and communicated with the journal.
Acknowledgements: Authors are thankful to Rector, Bhaderwah Campus, University of Jammu and Head, Department
of Environmental Sciences, University of Jammu for their administrative
support. The Department of Wildlife Protection, Govt. of Jammu and Kashmir is
duly acknowledged for its unwavering support and patronage in conducting such
explorations in the region. Muzaffar Ahmed, Asha Sohil, Vandana Dutt, Aasma Sharma and Ajaz Ansari are thanked for their help in field surveys.
Introduction
Otters, the semi-aquatic mammals
of the family Mustelidae with seven genera and 13
species are found in every continent except Australia and Antarctica. Eurasian
Otter Lutra lutra,
a European and Asian member of the Otter subfamily Lutrinae
is an elusive, solitary species with the largest range of any palearctic mammal
covering parts of three continents: Europe, Asia, and Africa (Corbet 1996).
Seven subspecies of Eurasian Otter (Bhattacharya et al. 2019) include L.l. nair
(Cuvier, 1823) found in southern India, Sri Lanka, Nepal, Bhutan, &
Myanmar; L.l. kutab
(Schinz, 1844) in northern India—Kashmir; L.l. aurobrunneus
(Hodgson, 1839) in Garhwal Himalaya & higher
altitudes in Nepal; L.l. monticolus (Hodgson, 1839) in Himachal
Pradesh, Sikkim, & Assam; L.l. barang (Cuvier, 1823) in southeastern Asia
(Thailand, Indonesia, & Malaysia); L.l.
chinensis (Gray, 1837) in southern
China & Taiwan, and L. l. lutra
(Linnaeus, 1758) in Europe & northern Africa. In India, it occurs in
the north (Ladakh, Jammu & Kashmir, Himachal
Pradesh, Uttarakhand), northeast (largely in Himalayan foothills), central
(Madhya Pradesh), east (Odisha), and southern India covering parts of Kerala,
Tamil Nadu, Karnataka, & Andhra Pradesh (Hussain 1993; Prater 1998). The
species has been recorded from the northern mountains of Pakistan, Punatshanghchu basin of Bhutan (Yoxon
& Yoxon 2019), and Nepal (Basnet et al. 2019;
Shrestha et al. 2021).
Eurasian Otter is regarded as a
flagship species and indicator of high-quality aquatic habitats (Macdonald
& Mason 1994; Cianfrani et al. 2011) that obtains
all its food from aquatic systems (Clavero et al.
2003; Krawczyk et al. 2016). They inhabit a wide variety of aquatic habitats,
including highland and lowland lakes, rivers, marshes, streams, swamp forests,
and coastal areas (Mason & Macdonald 1986). They occupy cold Himalayan
streams and rivers, much like their temperate cousins across Europe and Asia
(Prakash 2022), reaching 3,660 m in the Himalaya during summers (Prater 1971).
Most of the animal activity is restricted to a narrow land-water interface (Kruuk et al. 1994), as they prefer swiftly flowing upper
river sections (Kruuk 1995) which coincides with the
upward migration of the carp and other fish spawning.
The species is classified as
‘Near Threatened’ (Loy et al. 2022) on the IUCN Red List and is listed in
Appendix I of CITES (CITES 2023). The species became extinct in Japan in 1979
(Roos et al. 2015; Waku et al. 2016) and its populations in Europe and
developing Asian countries have drastically declined in recent years (Balestrieri et al. 2016; Jha et al. 2020). The species is
still hunted for their pelt, food, sport, and persecuted as a pest in many
Asian countries, particularly China, India, and Nepal (Gomez et al. 2016).
Along with habitat loss and pollution, climate change is a major cause of their
declining population (Gomez et al. 2016; Gupta et al. 2020). After a
catastrophic drop, otters are making a comeback across Europe (Loy et al. 2009,
2010; Romanowski et al. 2013), and other regions possibly as a result of legal
protection and the ban on Polychlorinated biphenyls (Loy et al. 2015).
The Indian Otter population is
severely fragmented across its distribution range, with isolated populations
primarily confined to protected areas (Hussain 1999; Nawab 2007, 2009; Nawab
& Gautam 2008) and high-altitude riverine ecosystems in the Indian
Himalayan region (Pal et al. 2021). It has so far been reported from Nayamjang Chu River, Arunachal Pradesh (Bhattacharya et al.
2019), forests of Madhya Pradesh including Balaghat
forest circle (Jena et al. 2016) and Satpura Tiger
Reserve (Joshi et al. 2016), Periyar Tiger Reserve in
Kerala & Kalakkad Mundanthurai
Tiger Reserve, Tamil Nadu (Raha & Hussain 2016),
Bhagirathi basin, Uttarakhand (Pal et al. 2021), and Sundargarh
forest division, Odisha (Palei et al. 2022). The
species was reported to occur in the Jammu & Kashmir divisions of the Union
Territory of Jammu & Kashmir (Ahmad et al. 2020). Jamwal
et al. (2016) and Shawl et al. (2008) confirmed its presence in Indus and its
tributaries in Ladakh. Following the credible
accounts of its historical presence in Neeru stream,
researchers from the Institute of Mountain Environment, Bhaderwah
conducted extensive investigations that included questionnaire surveys, direct
surveys, and camera trapping including a joint sign survey in collaboration
with Wild Otters Research Private Limited during July 2019. The current
communication describes the first photographic record of this elusive
semi-aquatic animal in Neeru stream.
Material
and Methods
Study area
The study area is characterized
by typical mountainous terrain comprised of high mountains, wide valleys,
cliffs and gorges, and vast alpine meadows. The region is drained by Neeru stream, a 30-km long linear hydro-morphological unit
(Image 1) that originates in Kailash Lake (3,900 m) and drains into the Chenab
River at Pul-Doda (848 m). The perennial stream
contributed by 13 major tributaries flows through a number of small villages,
semi-urban, and urbanised areas, with Bhaderwah being the largest settlement (Image 1). The
region is distinguished by its usual cold climate, with short summers and long
dry winters. The temperature varies with seasons and elevation and reaches
sub-zero during the winters. Precipitation is largely determined by topography,
ranging from 1,750 mm at lower and intermediate altitudes (<1,500 m) to 800
mm over 2,000 m. The vegetation varies from sub-temperate scrub at lower
elevations to pure conifers and broad leaved-conifer mixed at the mid, and
spruce-fir and kharsu oak at higher elevations
marking the tree line.
Field data collection
We conducted a questionnaire
survey in the upper Neeru stretch during 2016 and
2017 and found evidence of their historical presence. Following that, we
initiated primary surveys for direct and indirect sightings looking for fresh
sign (tracks; scats/spraints; evidence of foraging like remains of animal prey,
especially, fish scales or bones and cartilages) lodging and dens (Gallant et
al. 2008; Crimmins et al. 2009; Lesmeister &
Nielsen 2011; Schooley et al. 2012) along the main channel and its major
tributaries during 2019–2021. Although we were unable to establish a direct
sighting, we were able to locate a few latrines in 2020. Subsequently, we
deployed five infra-red cameras at three probable locations like the mouth of
dens, trails leading to dens, and stream banks near the latrine sites. The
cameras were placed roughly 100 m apart and were retained in the field for five
days from 17 to 21 October 2020.
Results
The questionnaire surveys of
2016–17 indicated that otters inhabited along the whole length of the Neeru stream and all of its tributaries. The animal is
locally known as ‘Huder’ or ‘Hud’.
According to the majority of respondents, the fish-eating animals resemble
mongooses with a somewhat greyer coat and bigger stature. When foraging, most
people described the sinuous up and down movement of a swimming otter, that
scans its surroundings with just its head above water. To ascertain the
presence of the animal, the surveys were conducted in July 2019, October 2020
and August 2021. On 15 October 2020, the team spotted a latrine mound with
dark, greasy poop at the mouth of the holt near Bhalla (33.060 oN to
75.626oE, 1,240 m). Five camera traps were deployed at three sites
which appeared to us as the probable dens of the otters. While sites 1 and 2
yielded no results, Site-3, the mouth of the den housing the latrine site,
captured many photographs of two adults and one sub-adult (Image 2), confirming
its presence. On 28 August 2021, while re-exploring the site, the team
discovered scratches and marks in a nearby narrow crevice that was presumably
used for resting and grooming (Image 3).
The species was identified as a
Eurasian Otter Lutra lutra
based on a dark brown dorsal coat with a pale silvery tinge on the neck,
rounded head with stiff white vibrissae around the muzzle, semi-webbed feet
with discernible toes, elongated body, and dorsoventrally flattened tail
(Hussain 2013; Menon 2014). Most of the images were captured during the early
morning. The location of otter sighting is characterised
by a small undisturbed narrow section of the stream with rocky banks, deep
caves and crevices and shore vegetation comprising young stands of Alnus nitida making
up the bulk of the riparian vegetation and Pinus roxburghii
along the upper dry slopes. The stream is home to Schizothorax
richardsonii and Glyptosternum
reticulatum, the former being abundant and most
relished fish in the region.
Discussion
A considerable decline in the
otter population in the Neeru stream over the past
two decades, as indicated in the questionnaire surveys, raises concerns about
the changing ecological dynamics of the stream. The sole sighting of the
family, however, raised hope of the species existence and survival in the
region. Since their presence goes unrecognised due to
their secretive, solitary, and nocturnal habits (Pal et al. 2021), our limited
survey does not rule out the presence of otter in other sections of the main
channel and that of tributaries those are pristine. Though the otters have wide
habitat preferences in terms of where they live, swim, hunt, and raise their
young (Kruuk 1995; Reid et al. 2013), their preferred
habitat is much more specific (Anoop & Hussain 2004). River topography
affects the prey availability and consequently the distribution of otters.
Otters largely prefer shallow braided river channels with shallow depth,
moderate current, patches of muddy and sand substrate on the shoreline, and
dense escape cover of vegetation in riparian habitats (Hussain & Choudhury
1997; Anoop & Hussain 2004; Acharya et al. 2010; Romanowski et al. 2013). Neeru being a typical hill stream offer but limited habitat
conditions with rocky banks, deep crevices, thin sand shoulders, dense escape
cover, and steep slopes. Several studies confirmed that otters avoid polluted
water and persist in low-anthropogenic landscapes (Romanowski et al. 2013; Calzada et al. 2022) though in low numbers (Baltrūnaitė et al. 2009). Bhaderwah,
a popular tourist destination over the years has experienced extensive urbanisation and infrastructure development, resulting in
degraded surface water quality of Neeru
stream over its whole course (Kumar et al. 2019, 2022). The stream serves
as a sink for urban wastes, notably the plastic trash that penetrates crevices
and holts during floods and clogs them. Stream bed mining for construction
materials fragments habitats hence threatening their existence. Jenkins &
Burrows (1980) and Macdonald & Mason (1983) revealed that poor-quality
habitats are occasionally visited by otters. Several incidents of retaliatory
killings, poaching, and predation by feral dogs have been reported by the
locals during the interactions. Having established its presence, the study
urges continued investigations on the species to better understand their
distribution, ecology, and threat status as well as to develop appropriate
conservation and management plans for its survival in the region.
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