| COUNTRY India - Rajasthan
NAME Keoladeo (Bharatpur) National Park
IUCN MANAGEMENT CATEGORY
II (National Park)
Natural World Heritage Site - Criterion iv
BIOGEOGRAPHICAL PROVINCE 4.08.04 (Indus-Ganges
Monsoon Forest)
GEOGRAPHICAL LOCATION Situated in eastern Rajasthan,
the park is 2km south-east of Bharatpur and 50km west of Agra. 27°07'-27°12'N,
77°29'-77°33'E
DATE AND HISTORY OF ESTABLISHMENT Established
as a national park on 10 March 1982. Previously the private duck shooting
preserve of the Maharaja of Bharatpur since the 1850's, the area was designated
as a bird sanctuary on 13 March 1956 and a Ramsar site in October 1981.
The last big shoot was held in 1964 but the Maharajah retained shooting
rights until 1972. Inscribed on the World Heritage List in 1985.
AREA 2,873ha
LAND TENURE Rajasthan State Government
ALTITUDE 174m
PHYSICAL FEATURES The area consists of a flat
patchwork of marshes in the Gangetic plain, artificially created in the
1850s and maintained ever since by a system of canals, sluices and dykes.
Normally, water is fed into the marshes twice a year from inundations
of the Gambira and Banganga rivers, which are impounded on arable land
by means of an artificial dam called Ajan Bund, to the south of the park.
The first time, usually in mid-July, is soon after the onset of the monsoon
and the second time is in late September or in October when Ajan Bund
is drained ready for cultivation in winter. Thus, the area is flooded
to an depth of 1-2m throughout the monsoon (July-September), after which
the water level drops. From February onwards the land begins to dry out
and by June only some water remains. For much of the year the area of
wetland is only 1,000ha. Soils are predominantly alluvial - some clay
has formed as a result of the periodic inundations.
CLIMATE During 1988, mean maximum temperature
ranged from 20.9°C in January to 47.8°C in May, while the mean temperature
varied from 6.8°C in December to 26.5°C in June. The diurnal temperature
variation ranged from 5°C in January to 50°C in May. Mean relatively humidity
varied from 62% in March to 83.3% in December. The mean annual precipitation
is 662mm, with rain falling on an average of 36 days per year. During
1988 only 395mm of rain fell during 32 wet days (Vijayan, 1989).
VEGETATION In a semi-arid biotype, the park
is the only area with much vegetation, hence the term 'Ghana' meaning
'thicket'. The principal vegetation types are tropical dry deciduous forest,
intermixed with dry grassland in areas where forest has been degraded.
Apart form the artificially managed marshes, much of the area is covered
by medium-sized trees and shrubs. Forests, mostly in the north-east of
the park, are dominated by kalam or kadam Mitragyna parvifolia,
jamun Syzygium cuminii and babul Acacia nilotica. Neem Azadirachta
inidca, probably introduced, is occasional. The open woodland is mostly
babul with a small amount of kandi Prosopis spicigera and ber Zizyphus
mauritiana. Scrublands are dominated by ber and kair Capparis decidua.
Piloo Salvadora oleoides and S. persica also occur scrubland
and are virtually the only woody plants found in areas of saline soil.
The aquatic vegetation is rich in species and is a valuable source of
food for waterfowl. Saxena (1975) lists the park's flora.
FAUNA Primates are rhesus macaque Macaca
mulatta and langur Presbytis entellus. Large predators are
absent, leopard Panthera pardus having been deliberately exterminated
by 1964, but small carnivores include Bengal fox Vulpes bengalensis,
jackal Canis aureus, striped hyena Hyaena hyaena, common
palm civet Paradoxurus hermaphroditus, small Indian civet Viverricula
indica, Indian grey mongoose Herpestes edwardsi, fishing cat
Felis viverrina (K), leopard cat F. bengalensis, jungle
cat F. chaus and smooth-coated otter Lutra perspicillata
numbering about 30 individuals (Haque and Vijayan, 1988). Ungulates include
blackbuck Antilope cervicapra (60)[30], chital Cervus axis
(350)[230-260], sambar C. unicolor[20], hog deer C. porcinus,
nilgai Boselaphus tragocamelus (480)[160-180] and wild boar Sus
scrofa [200-250] and feral cattle [950-1,000]. (The figures in brackets
refer to the number of animals counted in the 1980 census and those in
square brackets refer to the 1988 census (Vijayan, 1989)). Other mammals
include Indian porcupine Hystrix indica and Indian hare Lepus
nigricollis.
An estimated 65 million fish-fry are carried into the
parks water impoundments by river flooding every year during the monsoon
season, which provides the food base for large numbers of wading and fish-eating
birds (Milne, 1997). Some 364 species of bird have been recorded in the
park, which is considered to be one of the world's finest areas for birds,
with an unique assemblage of species. The park was the last known wintering
ground in India of the western population of Siberian crane Grus leucogeranus
(V). Despite reaching a decade-high total of 41 birds during the winter
of 1984-85 (ICBP, 1985) numbers have been steadily decreasing and in the
winter of 1993 and 1994, none were observed (K. Rao pers. comm., 1995).
In 1996, four birds wintered in the park, and in 1997 two adults and a
young bird were observed (Milne, 1997). There is only one other known
western population in Iran, but a thriving eastern population of some
1,350 cranes has recently been discovered wintering in Poyang Lake Nature
Reserve, Jiangxi, China.
The park's location in the Gangetic Plain makes it an
unrivalled breeding site for herons, storks and cormorants and an important
wintering ground for large numbers of migrant ducks. The most common waterfowl
are gadwall Anas strepera, shoveler A. clypeata, common
teal A. crecca, cotton teal Nettapus coromandelianus, tufted
duck Aythya fuligula, comb duck Sarkidiornis melanotos,
little cormorant Phalacrocorax niger, great cormorant P. carbo,
Indian shag P. fuscicollis, ruff Philomachus pugnax (probably
the most abundant wader), painted stork Ibis leucocephalus, white
spoonbill Platalea leucorodia, Asian open-billed stork Anastomus
oscitans, oriental ibis Threskiornis melanocephalus, darter
Anhinga melanogaster, common sandpiper Tringa hypoleucos,
wood sandpiper T. glareolaand green sandpiper T. ochropus.
Sarus crane Grus antigone, with its spectacular courtship dance,
is also found here. Among land birds is a rich assortment consisting of
warblers, babblers, bee-eaters, bulbuls, buntings, chats, partridges and
quails. Grey hornbill Tockus birostris and Marshall's iora Aegithina
nigrolutea are also present. There are many birds of prey including
the osprey Pandio haliaetus, peregrine Falco peregrinus,
Pallas' sea-eagle Haliaeetus leucoryphus (R), short-toed eagle
Circaetus gallicus, tawny eagle Aquila rapax, imperial eagle
A. heliaca (R), spotted eagle A. clanga and crested serpent
eagle Spilornis cheela. Greater spotted eagle has recently been
recorded breeding here, a new breeding record for the species in India
(Prakash, 1988a) and lesser spotted eagle Aquila pomarina hastata
nested in the park in 1986, the first nesting record for the species in
India for some time (Prakash, 1988b). Several other threatened avifauna
species occur, including Dalmatian pelican Pelecanus crispus (V),
spot-billed pelican P. philippensis (I), greater adjutant Leptoptilus
dubius (E), lesser adjutant L. javanicus (V), marbled teal
Marmaronetta angustirostris (V), Baikal teal Anas formosa (V),
Baer's pochard Aythya baeri (V), red kite Milvus milvus (K),
cinereous vulture Aegypius monochus (V) and sociable lapwing Vanellus
gregarius (R) (K. Rao pers. comm., 1995). Abdulali and Pandey (1978)
and Ali and Hussain (1982) provide checklists of birds recorded in the
park.
Reptiles include water snakes, Indian python Python
molurus (V), banded krait Bungarus fasciatus, green rat snake
Zaocys nigromarginatus, turtles (Lissemys punctatus, Trionyx
gangeticus, Kachuga tectum and Hardella thurgi) and
monitor lizard Varanus sp. Some 50 species of fish have been identified
(Kumar and Vijayan, 1988). Protozoa, zooplankton and macrobenthic oligochaeta,
Insecta and Mollusca have been studied with particular reference to drought
conditions (Mahajan et al., 1981a, b and c). A discussion
on the aquatic macroinvertebrates, terrestrial invertebrates, fish, herpetofauna,
birds and mammals is given in Vijayan (1989).
CULTURAL HERITAGE No information
LOCAL HUMAN POPULATION There are no local people
living within the park, but it is surrounded by 17 villages and the town
of Bharatpur is close by.
VISITORS AND VISITOR FACILITIES Food and accommodation
is available at Shanti Kutir Forest Lodge (64 beds), bookable through
the Forest Department, and the more expensive ITDC Forest Lodge (36 beds),
bookable through the Tourist Department. Boats can be hired and guides
knowledgeable about birds are available. There were 80,000 visitors in
1984. During 1994-95, an education/interpretation centre was established
at the park's entrance.
SCIENTIFIC RESEARCH AND FACILITIES The Bombay
Natural History Society has done considerable work in the area, including
the ringing of birds for the last 40 years. The society has recently intensified
its operations and has established a hydro-biological station to monitor
the ecology of the wetland. Particular attention will be given to any
in dramatic change in the vegetation following the ban on grazing. Limnological
studies have been carried out by the Zoology Department of the University
of Rajasthan, Jaipur. The park authorities are monitoring the bird populations.
A documentary film 'Indian birds of the monsoon' was produced by S. and
B. Breeden in 1979-1980. The park has considerable potential for education,
more so than other wetland sites in India, in view of it beingrelatively
near to the cities of Agra, Delhi and Jaipur. A bibliography of papers
etc. produced during 1988 is given in Vijayan (1989).
Between December 1992 and January 1995, a collaborative
project between the Governments of India and Russia, International Crane
Foundation and Wild Bird Society of Japan was set up to save the Siberian
crane. The project focused on releasing captivity bred cranes into the
wild, tracking migratory routes of common cranes, and building up the
resident crane population in the park. Although the project did not yield
the desired results, the successful survival of introduced cranes in the
park has given sufficient hope to develop a viable resident population
in the future (K. Rao pers. comm., 1995).
CONSERVATION VALUE This former duck-hunting
reserve of the Maharajas remains one of the major wintering areas for
large numbers of aquatic birds, including several threatened species from
Afghanistan, Turkmenistan, China and Siberia.
CONSERVATION MANAGEMENT The management objective
is to allow the area to flood and dry out annually, rather than be maintained
as a system of permanent marshes. Water for the wetlands is supplied from
a dam outside the park boundaries, usually some 15 million cu.m, and the
water levels are regulated to benefit waterfowl. If the wetland is in
danger of drying out completely, water can be pumped from four boreholes
to ensure the survival of some aquatic flora and fauna until the monsoon.
The boundaries are clearly delineated by a 32km long,
2m high stone wall, which totally encloses the park to prevent humans
and domestic livestock from trespassing. Due to the dense human settlement
surrounding the park, there is no possibility of creating a buffer zone.
The road from Bharatpur town, which bisects the park, has been closed
and relocated outside the boundaries. This has considerably reduced the
level of disturbance by visitors from the town. Grazing and the collection
of firewood and khus grass Vetiveria zizenoides were phased out
in 1983.
MANAGEMENT CONSTRAINTS Siberian crane, which
formerly occurred throughout the entire Indo-Gangetic plains of India,
is reported to no longer be found in the area. Its absence has been attributed
to hunting by nomadic tribes along the specie's 5,000 mile migration route
from Siberia to Bharatpur (K. Rao pers. comm., 1995).
Some 2,500 cattle and water buffalo were allowed in
the area up until November 1982 when grazing was banned. Predictably,
the ban led to a build up of local resentment, resulting in an attempted
forced entry into the park. Police opened fire and eight people were killed:
tensions still remain high. The absence of grazing is causing management
problems as vegetation, principally Paspalum distichum, a perennial
amphibious grass, blocks up the channels. The Rajasthan government has
rejected a proposal from the Bombay Natural History Society to allow limited
grazing, since this conflicts with the law (Earle, 1987). Furthermore,
recycled nutrients from the large quantity of dung deposited by livestock
probably supported considerable numbers of insects.
The presence of some 700 feral cattle within the park
is cause for concern as they compete with wildlife for valuable forage.
Larvae of the Lepidopteran Parapoynx diminutalis has also been
a serious pest, and considerably inhibited the growth of Nymphoides
cristatum during June-July 1986 (John and Nanjappa, 1988). High levels
of pollutants in Ajan Bund arebelieved to be responsible for the increasing
number of piscivorous birds seen in a dazed state and unable to fly. Fewer
birds were recorded in 1984 than in previous years. Four Sarus cranes
and 40 ring doves were found dead outside the park during 1988 and early
1989, possibly due to pesticide poisoning, and a study of the impact of
pesticide use in surrounding areas on the park has been initiated in addition
to studies on heavy metal contamination (Vijayan, 1989). Disturbance from
visitors can be a cause for concern, especially during the December and
January when visitors come to see the cranes.
A non-native water hyacinth Icornia species was
introduced in 1961, and has now proliferated to the extent that it is
blocking the artificial waterways and filling the impoundments. This is
significantly altering the habitat for many bird species, and is a serious
management problem. Atempts to control the species have been ineffectual
to date (Milne, 1997).
STAFF Under the Deputy Chief Wildlife Warden
are a research officer, forester, three rangers, 20 wildlife guards, clerks
and an accountant.
BUDGET During 1994-95, financial assistance
to the State of Rajasthan for development work in Keoladeo National Park
was to the tune of 2.39 million Rupees. A sizeable amount is also spent
by the State Government on establishment, management and maintenance and
development of facilities (K. Rao pers. comm., 1995).
LOCAL ADDRESSES
Deputy Chief Wildlife Warden, Keoladeo National Park,
Bharatpur, Rajasthan
REFERENCES
Abdulali, H. and Panday, J.D. (1978). Checklist of the
birds of Delhi, Agra and Bharatpur. Unpublished report.
Ali, S. (1953). The Keoladeo Ghana of Bharatpur (Rajasthan).
Journal of the Bombay Natural History Society 51: 531-536.
Ali, S. and Hussain, S.A. (1982). Studies on the movement
and population structure of Indian avifauna. Annual Report II. Bombay
Natural History Society, Bombay.
Breeden, S. and Breeden, B. (1982). The drought of 1979-1980
at the Keoladeo Ghana Sanctuary, Bharatpur, Rajasthan. Journal of the
Bombay Natural History Society 79: 1-37.
Breeden, S. and Breeden, B. (1982-1983). A year at Bharatpur's
Keoladeo National Park. Hornbill 1982 (3,4) and 1983 (1,2).
Earle, S. (1987). A sanctuary for birds. The India
Magazine 7: 60-69.
Government of India (1981). Document submitted at the
time of accession to the Ramsar Convention.
Grimwood, I.R. (1981). Impact of tourism on national
parks in India. WWF-India. Unpublished report. Pp. 15-20.
Haque, M.N. and Vijayan, V.S. (1988). Food habits of
the smooth Indian otter (Lutra perspicillata) in Keoladeo National
Park, Bharatpur, Rajasthan. IUCN Asian Otter Specialist Group Newsletter
No. 1.
ICBP (1985). World Birdwatch 7(1): 4.
Jackson, P. (1983). Crisis for birds and buffalos at
Bharatpur. Unpublished report. 3 pp.
John, G.M. and Nanjappa, C. (1988). Paraponyx diminutalis
Snellen (Pyralidae: Lepidoptera) as a serious pest of Nymphoides cristatum
in Keoladeo National Park, Baharatpur, Rajasthan. Journal of the Bombay
Natural History Society 85: 12.
Kumar, C.R.A. and Vijayan, V.s. (1988). On the fish
of Keoladeo National Park, Bharatpur (Rajasthan). Journal of the Bombay
Natural History Society 85: 44-49.
Lall, S. and Raman, L. (1994). The Siberian Cranes'
Last Indian Winter. WWF Features. World Wide Life Fund-India. 3
pp.
Landfried, S.E. (1991). Western Flocks of Siberian Cranes
at the Brink of Extinction. Natura Summer 1991. Pp 4-6.
Mahajan, C.L., Sharma, S.P., Sharma, S.D. and Arora,
N.K. (1981a). Protozoan fauna of a wetland ecosystem (Bharatpur Bird Sanctuary)
during drought conditions. International Journal of Ecology and Environmental
Sciences 7: 131-138.
Mahajan, C.L., Sharma, S.P., Sharma, S.D. and Arora,
N.K. (1981b). Changes in zooplankton populations in a wetland ecosystem
due to drought. International Journal of Ecology and Environmental
Sciences 7: 139-143.
Mahajan, C.L., Sharma, S.P., Sharma, S.D. and Arora,
N.K. (1981c). Benthic fauna in a wetland ecosystem (Ghana Bird Sanctuary,
Bharatpur) subjected to drought stress. International Journal of Ecology
and Environmental Science 7: 145-148.
Milne R.C. (1997) Mission Report: South Asia meeting
to review status conservation of world natural heritage and design and
cooperative plan of action. 16-19 January 1997, New Delhi, India.
Prepared for the World Heritage Centre, UNESCO. Unpublished Report, 7pp.
Prakash, V. (1988a). Greater spotted eagle (Aquila
clanga) breeding in Keoladeo National Park, Bharatpur. Journal
of the Bombay Natural History Society 85: 415.
Prakash, V. (1988b). Lesser spotted eagle (Aquila
pomarina hastata) nesting in Keoladeo National Park, Bharatpur. Journal
of the Bombay Natural History Society 85: 614.
Saxena, V.S. (1975). A study of the flora and fauna
of Bharatpur Bird Sanctuary. Department of Tourism, Jaipur, Rajasthan.
Spillett, J.J. (1967). A report on wild life surveys
in North India and southern Nepal: the large mammals of the Keoladeo Ghana
Sanctuary, Rajasthan. Journal of the Bombay Natural History Society
63: 602-607. (Unseen)
Vijayan, V.S. (1989). Keoladeo National Park ecology
study. Annual Report 1988. Bombay Natural History Society. 123 pp.
DATE October 1985, updated May 1989 and May
1990, August 1995, April 1997.
|