Journal of Threatened Taxa |
www.threatenedtaxa.org | 26 February 2021 | 13(2): 17832–17836
ISSN 0974-7907 (Online) | ISSN 0974-7893
(Print)
https://doi.org/10.11609/jott.5610.13.2.17832-17836
#5610 | Received 09 December 2019 | Final
received 19 January 2021 | Finally accepted 27 November 2019
High altitude wetland migratory
birds in the Sikkim Himalaya: a future conservation perspective
Prem K. Chhetri 1, Kusal Gurung 2, Thinlay
Namgyal Lepcha 3 &
Bijoy Chhetri 4
1 Forest,
Environment and Wildlife Management Department, Government of Sikkim, Deorali, Sikkim 737102, India.
2 Revenue
Officer/Assistant Director, Sub-Division Office, Pakyong,
East Sikkim, Sikkim 737106, India.
3 Human
Resource Development Department, Govt. of Sikkim, Singhik
Sentam, North Sikkim, Sikkim 737116, India.
4 G.B. Pant
National Institute of Himalayan Environment and Sustainable Development, Sikkim
Regional Centre, Pangthang, East Sikkim, Gangtok, Sikkim 737101, India.
4 Bombay
Natural History Society, Hornbill, Dr. Salim Ali
Chowk, Shaheed Bhagat Singh Road, Mumbai, Maharashtra 40001, India.
1 chhetriprem22@gmail.com,
2 korongee@gmail.com, 3 thinlaylepcha37@gmail.com, 4
chhetribijoy@yahoo.co.in (corresponding author)
Editor: Hem Sagar Baral, Charles Sturt
University, Albury, Australia. Date of publication: 26 February
2021 (online & print)
Citation:
Chhetri, P.K., K. Gurung, T.N. Lepcha & B.
Chhetri (2021). High altitude wetland migratory birds in the Sikkim
Himalaya: a future conservation perspective. Journal of Threatened Taxa 13(2): 17832–17836. https://doi.org/10.11609/jott.5610.13.2.17832-17836
Copyright: © Chhetri et al. 2021. 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: Self Funded.
Competing interests: The authors declare no competing interests.
Acknowledgements: We are grateful to the Forest Environment and Wildlife
Department, Govt. of Sikkim and Barapathing Rage (T)
for the support during the field study. Lastly, field suggestion and encouragement
by Dr. H.K. Badola, Dr. B.K. Acharya, and friends will be highly appreciated.
The Trans-Himalaya contain the most glaciated terrain
outside of the polar regions (Owen 2017), and they generate and recharge high
altitude wetlands (HAWs) via melting.
HAWs are typically situated above 3,000m, between the tree line and permanent
snow line (Khan & Baig 2017). Sikkim Himalaya wetlands play a vital
role for migratory birds by providing breeding and winter grounds (Chandan et
al. 2008; Ganguli-Lachungpa et al. 2011). Many migratory birds are attracted to the
HAWs of the state, based on the compilation report of the Sikkim Forest
Department over the past two decades, observed in the high altitude wetlands in
northern and eastern Sikkim (Ganguli-Lachungpa et al.
2011). It is reported that Ruddy
Shelduck Tadorna ferruginea (Pallas,
1764) visits high altitude lakes and marshes of the Sikkim Himalaya for
breeding (Ganguli-Lachungpa 1990a, 1992). Many wetland migratory birds are reported
from Sikkim Himalaya, viz.: Osprey Pandion haliaetus (Linnaeus,
1758), Little Grebe Podiceps ruficollis (Pallas, 1764), Common Coot Fulica atra (Linnaeus,
1758), Bar-headed Goose Anser indicus (Latham,
1790), Northern Pintail Anas acuta (Linnaeus,
1758), Mallard Anas platyrhynchos (Linnaeus, 1758), Baer’s
Pochard Aythya baeri (Radde, 1863), Tufted Duck Aythya
ferina (Linnaeus, 1758) (Ganguli-Lachungpa 1990a,b, 1994; 1998; 2003; Chettri et al. 2005);
Pallas’s Gull Larus ichthyaetus (Pallas, 1773) (Sharma & Bhat
2016), Common Pochard Aythya ferina (Linnaeus, 1758), Great
Cormorant Phalacrocorax carbo (Linnaeus,
1758); Goosander Mergus merganser (Linnaeus,
1758), and Black-necked Grebe Podiceps
nigricollis (Brehm, 1831) (Acharya &
Vijayan 2011; Ganguli-Lachungpa 1990a; 1992). For better preservation and conservation of
HAW areas, an initiative has been started by the Sikkim Forest Department, in
collaboration with local NGOs with the formation of a Pokhari
Sanrakshan Samiti (PSS) on 24 May 2017. The three potential Ramsar
sites have been proposed in the Sikkim Himalaya, the detailed information
sheets (RIS: 2009–2012 version) have been submitted to the Ministry of
Environment, Forest and Climate Change, India in 2011. The names of the proposed Ramsar
sites are; Khecheopalri-Khangchendzonga-Lonak
Complex, Tsomgo-Phedang Tso Complex, and Tso Lhamo plateau-Lashar-Yumesamdong-Tembao Complex (See Forest Environment and
Wildlife Management Department 2015).
Further, the detailed agenda regarding the high altitude Ramsar sites of the Sikkim Himalaya precisely discussed
(see O’neill 2019). The record of new species such as Ferruginous
Duck Aythya nyroca
(Near Threatened) and Brown-headed Gull Chroicocephalus
brunnicephalus (Least Concern) indicates a
potential habitat for wetland migratory birds in the Sikkim Himalaya. Therefore, immediate intervention is needed
for improved conservation and habitat management for migratory birds in the
Sikkim Himalaya through community-based conservation.
Sikkim Himalaya, a total area of 7,096km2,
is a part of eastern Hindu-Kush Himalaya contiguous with eastern Himalaya. It
lies between geographical coordinates 27.063–28.126 0N &
88.061–88.955 0E. The
elevation varies from 284 to 8,586 m, with a picturesque landscape of Mt. Khangchendzonga (8,586m).
The geopolitical area of Sikkim is surrounded by Nepal (west), Tibet
(north), Bhutan (east), and Tibet (east), and Darjeeling District of West
Bengal (south). Sikkim Himalaya has a
rich cultural and biologically diversity.
The surveys were conducted from December 2017 to April 2018 to assess
the species richness of the high altitude wetland migratory birds in the Sikkim
Himalaya. The four high altitude wetlands (lakes) were selected from East
Sikkim as a case study—Tsomgo (approx. 24.47ha in
area, 3,753m), Hangu (approx. 58ha, 4,237m), Mementsho (approx. 42ha, 3,810m), and Phedang
Tso (approx. 45ha, 4,600m) (Figure 1). A
2-km line transect was laid down on both sides of the lakes to study the high
altitude wetland migratory birds. The
individuals of the species with the latitudes, longitudes, and altitudes were
recorded within the transects. We used latitudes and longitudes of the species
for developing a digital elevation model of the study area (Figure 1). A line-transect sampling is a strategy commonly
used to assess richness and abundance of large diurnal vertebrates in forests
(de Thoisy et al. 2008). For the study, the permission obtained from
the Forests, Environment and Wildlife Management Department, Government of
Sikkim (Permit no. Home/Confd/149/2017/3414).
Total of 15 wetland migratory bird species were
recorded from the study area. Out of the
15 species, two species—Brown-headed Gull and Ferruginous Duck—were
recorded from the Kyongnosla Alpine Sanctuary
(27.332N, 28.827E, 4,000m) of the Sikkim Himalaya (Image 1 & 2). The Ruddy Shelduck was found breeding in
Sikkim HAWs. The species recorded
belonged to five bird families, 10 species encountered under Anatidae family followed by Podicipedidae
(two species), and rest of the families having single species each. The species richness of the migratory birds
in Phedang Tso or Elephant Lake (14 species) followed
by Hangu Lake (12 species), Tsomgo
Lake (seven species), and Mementsho Lake (two
species). Ruddy Shelduck was recorded from the highest elevation in the study
area followed by Northern Pintail, Tufted Duck, Great Crested Grebe Podiceps cristatus, and so on (Table 1).
Many migratory birds have been recorded from the
Sikkim Himalaya indicating that the Sikkim HAWs offer potential suitable
breeding and winter grounds.
Brown-headed Gull and Ferruginous Duck first reported from the high
altitude wetlands is a new record to the state.
The Brown-headed and Ferruginous Duck have been reported from other
parts of India (Mishra & Humbert-Droz 1998;
Mukherjee et al. 2002; Choudhury 2010).
Maximum species richness of migratory birds was observed in Phedang Tso (Elephant Lake) in the study area. The area is out of anthropogenic pressure
(like tourism activity) and falls under the restricted defence area and healthy
undergrowth vegetation as compared to the other sites. The other lakes, Tsomgo
(approx. 24.47ha, 3,753m), Mementsho (approx. 42ha,
3,810m) and Hangu (approx. 58ha, 4,237m) are under
the disturbance of tourism. Compared to
other states of India, having a small geographical area, the Sikkim Himalaya
offers a hub for avian species; over 550 birds recorded from the landscape (Ali
1962; Acharya & Vijayan 2011)
including migratory birds (Ganguli-Lachungpa et al.
2011). It is paramount to identify
wetlands in the Tibetan Plateau of the Central Asian Flyway to conserve
migratory birds because the birds need to refuel at these points to cross the
Himalaya (Namgail 2017). The HAWs (lakes) of the Sikkim Himalaya,
however, considered as sacred sites, makes their conservation the top priority
(Chandan et al. 2008). Hitherto, Sikkim
HAWs are under pressure of increasing tourism activities (Mazumdar et al.
2011). Worldwide, most of the migratory
birds threatened by wetland habitat loss on its breeding and winter grounds
(Ali & Ripley 1983; Scott & Rose 1996; Clements 2007; Grimmett et al. 2008).
Appreciating the importance of globally threatened birds found in the
Eastern Himalaya, 11 Important Birds Area or IBAs across the Sikkim Himalaya
have been recognized by the government of Sikkim in 2003 for the conservation
initiative (Ganguli-Lachungpa et al. 2011). Such actions will help to conserve the high
altitude wetlands of Sikkim Himalaya and migrating birds as well.
Table 1. Species
richness of migratory waterfowl in the respective high altitude wetlands of the
Sikkim Himalaya. (‘+’—present |
‘-‘—absent)
|
Family |
Common name |
Scientific name |
Phedang Tso (Elephant lake) |
Mementsho Lake |
Hangu Lake |
Tsomgo Lake |
IUCN RL status |
Estimated extent of occurrence (EOO) (km2)
based on IUCN, 2018 |
Popula-tion trend based on IUCN, 2018 |
Abundance (no. of individuals in the
lakes) |
1 |
Anatidae |
Ruddy
Shelduck |
Tadorna ferruginea Pallas |
+ |
+ |
+ |
+ |
LC |
37900000 |
Unknown |
100 |
2 |
Anatidae |
Goosander |
Mergus merganser Linnaeus |
+ |
|
|
+ |
LC |
77900000 |
Increasing |
4 |
3 |
Rallidae |
Common
Coot |
Fulica atra Linnaeus |
+ |
_ |
_ |
_ |
LC |
137000000 |
Increasing |
1 |
4 |
Anatidae |
Mallard |
Anas platyrhynchos Linnaeus |
+ |
_ |
+ |
_ |
LC |
127000000 |
Increasing |
6 |
5 |
Anatidae |
Eurasian
Wigeon |
Mareca penelope Linnaeus |
+ |
_ |
+ |
+ |
LC |
34900000 |
Decreasing |
12 |
6 |
Anatidae |
Tufted
Duck |
Aythya fuligula Linnaeus |
+ |
_ |
+ |
+ |
LC |
34900000 |
Stable |
50 |
7 |
Anatidae |
Common
Teal |
Anas crecca Linnaeus |
+ |
_ |
+ |
+ |
LC |
81700000 |
Unknown |
20 |
8 |
Phalacrocoracidae |
Great
Cormorant |
Phalacrocorax carbo Linnaeus |
+ |
+ |
+ |
+ |
LC |
323,000,000 |
Increasing |
6 |
9 |
Anatidae |
Northern
Pintail |
Anas acuta Linnaeus |
+ |
_ |
+ |
+ |
LC |
69100000 |
Decreasing |
12 |
10 |
Podicipedidae |
Black-
necked Grebe |
Podiceps nigricollis Brehm |
_ |
_ |
+ |
_ |
LC |
155000000 |
Unknown |
1 |
11 |
Podicipedidae |
Great
Crested Grebe |
Podiceps cristatus Linnaeus |
+ |
_ |
+ |
+ |
LC |
152000000 |
Unknown |
20 |
12 |
Anatidae |
Bar-headed
Goose |
Anser indicus Latham |
+ |
_ |
_ |
_ |
LC |
5260000 |
Decreasing |
2 |
13 |
Anatidae |
Gadwall |
Mareca strepera Linnaeus |
+ |
_ |
_ |
_ |
LC |
73100000 |
Increasing |
7 |
14 |
Anatidae |
Ferruginous
Duck |
Aythya nyroca Güldenstädt |
+ |
_ |
+ |
_ |
NT |
25900000 |
Decreasing |
3 |
15 |
Laridae |
Brown-headed
Gull |
Chroicocephalus brunnicephalus Jerdon |
+ |
_ |
+ |
_ |
LC |
851000 |
Stable |
35 |
For
figure & images - - click here
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