Status
of wetland birds of Chhilchhila Wildlife Sanctuary,
Haryana, India
Parmesh Kumar 1 &
S.K. Gupta 2
1,2 Department of Zoology,
University College, Kurukshetra University, Kurukshetra, Haryana 136119, India
1 parmeshkuk@rediffmail.com
(corresponding author), 2 sanjeevkuk@gmail.com
doi: http://dx.doi.org/10.11609/JoTT.o3158.3969-76 | ZooBank: urn:lsid:zoobank.org:pub:43DCABD3-C5F6-4629-8603-FBDE9FA67AC6
Editor: Rajiv S. Kalsi,
M.L.N. College, Haryana, India Dateof publication: 26 March 2013 (online & print)
Manuscript details: Ms #
o3158 | Received 11 April 2012 | Final received 04 December 2012 | Finally
accepted 08 March 2013
Citation: ParmeshKumar & S.K.Gupta (2013).Status of wetland birds of ChhilchhilaWildlife Sanctuary, Haryana, India. Journal of Threatened Taxa5(5): 3969-3976; doi:10.11609/JoTT.o3158.3969-76.
Copyright: © Kumar & Gupta
2013. Creative Commons Attribution 3.0 UnportedLicense. JoTT allows unrestricted use of this
article in any medium, reproduction and distribution by providing adequate
credit to the authors and the source of publication.
Funding: University Grants Commission,
New Delhi [No.F.8-2(143)/2011(MRP)/NRCB)]
Competing Interest: None.
Acknowledgements: The financial support received through a
minor research project from University Grants Commission, New Delhi, is
gratefully acknowledged.
Abstract: The Chhilchhila Wildlife Sanctuary (76036’–76046’E
& 29052’–30000’N), situated in Kurukshetra District of Haryana provides an important
wintering ground for a diverse range of wetland birds. This study was carried out from April
2009 to March 2012 to document the diversity of wetland birds. Altogether 57 species of wetland birds
belonging to 37 genera and 16 families were recorded from the study area.
Family Anatidae dominated the wetland bird community
with 13 species. Among recorded
species, 33 were winter migrants, two summer migrants
and 22 were resident species. The
winter migratory birds did not arrive at this wetland in one lot and at one
time. Instead, they displayed a
definite pattern specific to species for arrival and departure. They appeared at the wetland during
mid-October and stayed up to early April. The composition of birds in major feeding
guilds in the study area showed that the insectivore guild was the most common
with 35.09% species, followed by carnivore (29.82%), omnivore (19.30%),
herbivore (10.53%) and piscivore (5.26%). Among the birds recorded in this study
area, Darter (Anhinga melanogaster) and Painted Stork (Mycteria leucocephala)
were Near Threatened species. Comb Duck (Sarkidiornis melanotos), listed in Appendix II of CITES, was
also spotted in the sanctuary. The
spotting of these threatened bird species highlights the importance of Chhilchhila Wildlife Sanctuary as a significant wetland
bird habitat in Haryana. However,
anthropogenic activities like fire wood collection, livestock grazing, cutting
of emergent and fringe vegetation and improper management of the wetland are
major threats to the ecology of this landscape.
Keywords:Birds, Chhilchhila, diversity, Haryana, wetland.
For
figures, images, tables -- click here
Apart from their beauty,
recreational and economic importance, wetland birds are excellent indicators of
the general health of an ecosystem and measure of its biodiversity. Out of 310 species of wetland birds found
in India (Kumar et al. 2005), almost half of these are migratory and visit
India from their breeding grounds in China, Russia, central Asia, Tibet and
from across the entire range of the Himalaya. The availability of feeding and roosting
habitats is very important for these migratory species, which in some cases
migrate up to thousands of kilometers. As wetlands provide a wintering ground for many trans-equatorial species
of migratory birds, several wetlands in the country have been identified as being
internationally significant under the RamsarConvention. However, wetlands in India, are facing tremendous anthropogenic pressures (Prasad
et al. 2002), which can adversely influence the structure of bird communities (Kler 2002; Verma et al. 2004;
Reginald et al. 2007).
Birds inhabiting wetlands for
feeding, breeding, nesting or roosting are broadly defined as water birds. This comprises bird groups commonly
called waterfowl and waders. In
addition, several other bird groups like kingfishers,raptors and some passerines are also ecologically dependent on wetlands, hence
known as wetland dependent and associated birds (Kumar et al. 2005). In this paper, water birds, wetland
dependent and associated birds are collectively termed as wetland birds.
Monitoring of wetland birds
provides valuable information on the ecological health and status of wetlands
and can be a vital tool for developing awareness regarding the conservation
value of the wetlands. The
importance of local landscapes for conservation of avifauna can only be
understood by knowing the structure of the bird community of that region (Kattan & Franco 2004). Due to its unique geographical location,
a large number of water birds from Europe and Siberia spend a part of their
winter sojourn in the ponds, lakes and canals of Haryana. However, few studies have been carried
out on the status and diversity of wetland birds of Haryana (Bahuguna et al. 2008; Kumar & Gupta 2009; Tak et al. 2010). The Chhilchhila Wildlife Sanctuary (CWS)
situated in Kurukshetra District of Haryana provides
an excellent habitat for avifauna in the form of a water body with marshy plant
growth, terrestrial platforms, earth mounds having scattered trees and bushy
vegetation. Several migratory birds
visit this lake every year during winter. Keeping in view the conservation value of wetland birds, systematic
efforts were made during April 2009–March 2012 with the objective to have
an overview of the diversity and threats to wetland birds in this landscape.
Materials and Methods
Chhilchhila Wildlife Sanctuary (76036’–76046’E
& 29052’–30000’N) is located at a distance of
about 20km from Kurukshetra University towards west
in Kurukshetra District of Haryana, India (Fig.
1). It has a shallow water body
having an embankment of stabilized soil. It is a rain-fed lake, and therefore, the
volume of water keeps on changing depending on the season and the amount of
rainfall received. The depth of the
water varies from 4.5m in rainy season to 1.8–2.7 m in summer. There is a temple located on the edge of
the sanctuary, which is devoted to a local deity. Spread-out over an area of
about 28.7ha, the sanctuary provides varied habitats for a diverse range of
resident and migratory wetland birds with marshy plant growth, terrestrial
platforms, earth mounds with scattered trees, bushy vegetation and surrounding
fertile agricultural fields. The
predominating vegetation of the sanctuary is typically the dry deciduous
type. Common tree species are Acaciaarabica, Azardirachta indica, Zizyphus jujuba, Eucalyptus sp., Cassia tora,Ficus benghalensis, Ficus religiosa, Dalbergia sissoo, Prosopis cineraria and Prosopis juliflora. The dominant shrubs are Capparis deciduas, Calotropis procera, Adhatoda vasica, Alhagi maurorum and Xanthium strumarium, while Parthenium, Amaranthus spinosus, Chenopodium ambrosiodes, Achyranthes aspera, Malvastrum sp. and Boerhavia diffusa are
the prominent weeds in the study area. Aquatic plants in the lake are Hydrilla sp., Typha sp., Cyperus sp., Azolla sp. etc. The climate of Kurukshetrais tropical monsoonal. There are
three major seasons i.e. rainy (July–September), a cool dry (October
–February) and the hot dry season (March–June). Temperature varies from a high of 450C in summer to a
low of 30C in winter. The
normal annual rainfall is 582mm.
Observations
were made during July 2009–June 2011 with April 2009–March
2012. Regular surveys were done by
systematically walking on fixed routes through the study area. The birds were observed during the peak
hours of their activity from 0600–1000 hr and
from 1600–1800 hr with the aid of 7×35
Nikon binoculars. However, opportunistic records were also collected during
other time periods of the day. Birds seen were recorded along with habitat type, season and frequency
of sightings of a particular species. Photographs were taken whenever possible (Images 1–3).
Identification of birds was done using field guides (Ali & Ripley 1987; Grimmett et al. 1999), and only those species with
confirmed identity are reported in this paper. The checklist was prepared using
standard common and scientific names of the birds following Manakadan& Pittie (2001). Residential status of the birds as
resident, winter visitor and summer visitor has been assigned strictly with
reference to the study area on the basis of presence or absence method. The status of the recorded bird species
was established on the basis of frequency of sightings following Kumar &
Gupta (2009) as common recorded 9–10 times out of 10 visits, fairly
common recorded 6–8 times out of 10 visits, uncommon recorded 3–5
times out of 10 visits, rare recorded 0–2 times out of 10 visits. Feeding guilds were classified on the
basis of direct observations and available literature (Ali & Ripley
1987). The conservation status of
the bird species was assessed according to the Wildlife Protection Act, 1972,
CITES (2002) and IUCN (2010). Data
on threat factors were collected by direct observation and personal interviews
with local people.
Results and Discussion
Fifty seven species of wetland birds
belonging to 37 genera and 16 families were recorded from the Chhilchhila Wildlife Sanctuary from April 2009 to March
2012. The checklist of recorded
bird species along with their abundance, feeding guilds, residential and
conservational status is given in Table 1. The family Anatidae represented by 13 species, dominated the wetland bird community of the study
area (Fig. 2). It accounted for
22.81% of the total number of wetland bird species of the sanctuary. Among the recorded species, 33(58%) were
winter migrants, 2(3%) summer migrants and 22(39%) were resident species (Fig.
3). The status of some bird species
like Spot-billed Duck, Common Moorhen, Great Cormorant, Grey Heron, Large Egret
and Median Egret observed in Chhilchhila Wildlife
Sanctuary was different from their Haryana State status (Taket al. 2010). The summer visitors,
namely Cotton Teal Nettapus coromandelianus and Lesser Whistling Duck Dendrocygna javanica were
spotted during summer seasons from April to August. The winter migratory birds displayed a
definite pattern specific to species for arrival at and departure from the
wetland. They appeared at the
wetland from mid October and stayed up to April. The peak of winter population of
migratory birds was observed during the months of January and February. The present study revealed that NorthernShoveller Anas clypeata, Northern Pintail Anas acuta, Common Teal Anas crecca, Common Pochard Aythya ferina, Common
Coot Fulica atraand Gadwall Aythya ferinaarrived in October; Spot-billed Duck Anas poecilorhyncha, Mallard Anas platyrhynchos and Comb Duck Sarkidiornis melanotos arrived in November. As far as the departure time was
concerned, Mallard generally departed in February. Birds like Spot-billed Duck,
Common Pochard, Eurasian Wigeon Anas Penelope, Tufted Pochard Aythya fuligula and Red-crested Pochard Rhodonessa rufinadeparted in March. Common Coot,
Northern Shoveller, Northern Pintail, Common Teal and
Gadwall departed as late as April. Based on the frequency of sightings, two species were rare, 13 uncommon,
21 fairly common and 21 common. The
basic requirements of migratory birds at their wintering ground are adequate
food supply and safety (Lakshmi 2006), which are fulfilled by this wetland as it
was situated amidst fertile agricultural fields. The composition of birds in major
feeding guilds in the study area showed that the insectivore guild was the most
common with 36.84% species (Fig. 4), followed by carnivore (29.82%), omnivore
(19.30%), herbivore (10.53%) and piscivore(3.51%). The diversity of the
wetland birds documented during the present study may be due to the presence of
a wide spectrum of feeding niches. The wetland birds are in general heterogeneous in their feeding habits
(Ali & Ripley 1987). Thus
wetland birds exploit a variety of habitats and depend upon a mosaic of
microhabitats for their survival. Many
studies have demonstrated the importance of habitat heterogeneity in wetland
bird richness and abundance (Svingen & Anderson
1998; Edwards & Otis 1999; Fairbairn & Dinsmore2001; Riffel et al. 2001; Zárate-Ovandoet al. 2008; Datta 2011). In the present study, irrigated
agricultural fields surrounding the sanctuary, with scattered trees probably
provided shelter and suitable foraging grounds for the wetland birds. This habitat by supporting different
food sources like fish, crustaceans, invertebrates, water plants and plankton
further adds to the diversity of wetland birds (Basavarajappa2006). The population of some of
the birds such as Black-winged Stilt and Little Cormorant was found to be high
in winter, but a couple of birds observed in summer and monsoon confirmed their
status as residents. Among the
birds spotted in this study area, Darter Anhinga melanogaster (Birdlife
International 2012a) and Painted Stork Mycteria leucocephala (Birdlife International 2012b) are
Near Threatened species. Comb Duck,
a bird species listed in Appendix II of CITES was also spotted in the
Sanctuary. The spotting of these
threatened bird species highlights the importance of ChhilchhilaWildlife Sanctuary as an important staging and wintering ground for wetland
birds.
The avian heritage of this
landscape is under threat due to increased anthropogenic activities resulting
in habitat destruction and fragmentation. It is an alarming sign for conservation of the avian diversity of this
landscape. Direct observations as
well as personal interviews with local people during surveys revealed that
anthropogenic activities like livestock grazing, soil digging, encroachment,
use of forest wood as a source of fuel by local people, cutting of emergent and
fringed vegetation are some of the major threats to the biodiversity of this
landscape (Image 4–7). The
wetland needs to be patrolled to minimize disturbance, in particular during the
breeding season. The only source of
water in the lake is rain water and uncertainty in the
amount of rainfall coupled with decreased inflow of water from surrounding
agricultural fields due to intensive agriculture is also posing a threat to the
richness of biodiversity in the sanctuary. Thus, for sustainable upkeep of the wetland, alternative arrangements of
water supply from the nearby canal are required. Regular surveys related to waterbird species diversity and awareness of the local
people should be conducted for a detailed assessment of the wetland.
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