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Blue Bull or Nilgai (Boselaphus tragocamelus Pallas, 1766)

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11
Wildlife and Protected Areas
Vol.07
No.1 2004
Ungulat
es
I
ndia
I.
To'i
Wildlife Institute of India
INDIA
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Citation: Sankar, K and Goyal, S.P. (Eds.) 2004. Ungulates of India. ENVIS Bulletin: Wildlife
and Protected Areas, Vol. 07, No. 1. Wildlife Institute of India, Deheradun, India. Pp. 448.
Citation for individual chapter. Sharma, K., and Rahmani, A.R. 2004. Four horned antelope
or Chowsingha
(Tetracpn6 quad *vris
Blainvill1e). Pp. 53-60. In: K. Sankar and S.P. Goyal (Eds.)
Ungulates of India. ENVIS Bulletin: Wildlife and Protected Areas, Vol. 07, No. 1. Wildlife
Institute of India, Deheradun, India. Pp. 448.
ENVIS Bulletin: Wildlife and Protected Areas, Vol. 07. No. 1. Printed in 2007.
Envis
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guIletinis
also available on the internet at
WIT website: http://www wii.govin/envhome/eindex
Species illustrations are by Centre for Environmentl Education (CEE), Ahmedabad, India.
Photo Credits:
Asian wild buffalo, Barking deer, Indian wild ass, Nilgiri tahr, Rhinoceros (WII Photo Library)
Blue bull, Hog deer, Sambar (K. Sankar)
Indian gazelle (J. Van Gruisen), Four horned antelope (S.P. Goyal), Brow antlered deer (S.A. Hussain),
Wild pig (J.S. Jalal), Indian antelope (Y.V. Jhala), Pygmy hog (G. Narayan), Soptted deer (B. Pandav),
Indian bison (M.K.S. Pasha), Mouse deer (S. Prasad), Swamp deer (Q. Qureshi)
Leaf deer (www.animalinfo.org/species/artiperi/muntputa.htm)
Envis&lletiq
. WII ENVIS Centre on Wildlife and Protected Areas
Nilgai
BLUE BULL OR NILGAI
(Boselaphus tragocamelus
Pallas, 1766)
K. Sankar
, A.J.T. Johnsingh
and B
. Acharya
Order
Family
Sub-Family
Tribe
Genus
Species
Common name
Artiodactyla
Bovidae
Bovinae
Boselaphini
Boselaphus
B. tragocamelus
Nilgai, Blue bull
Conservation Status
WPA (1972)
IUCN RED DATA BOOK
CITES
INTRODUCTION
Schedule III
Lower risk
Not listed
Nilgai are the largest antelopes in Asia, about the size of a horse. Brander
(1923) reported a 270 kg bull in central India. Walker (1968) reported
that an adult nilgai weighs about 200 kg. Prater (1971) opined that bulls
could weigh up to 270 kg. In Texas, 39 bulls averaged 241 kg and 23
adult cows 169 kg (Sheffield
et al.
1983). An adult male stands 130 to
140 cm at the shoulder (Walker 1968, Prater 1971). Sale
et al.
(1988)
reported shoulder height of eight bulls ranging from 130 to 150 cm (mean
138.4 cm) and for five cows from 100 to 130 cm (mean 116.8 cm), in
Punjab, India. Bulls in Texas averaged 180 cm in length, 160 cm in
chest girth, and 120 cm height at the shoulders. The corresponding
dimensions for cows were 170 cm, 130 cm, and 120 cm respectively
(Sheffield
et al.
1983). Only male nilgai have horns which are short (15-
20 cm), stout, conical and smooth in nature.
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29
Nilgai calves and cows are light brown in colour. The light brown colour
of male calves begins to darken by the tenth month and they develop
black legs and brownish grey shoulders by 18 months. Adult nilgai bulls
are steel-grey or blue grey in colour with black legs, which is developed
by the fourth year (Sheffield
et al.
1983). All individuals have dark and
white markings on their heads, ears, under-parts, fetlocks, and tail, and
prominent white vibrissa spots on the head. At the midpoint on the ventral
side of the neck is a tuft of hair, more pronounced in bulls than in cows
(Sheffield et al.
1983).
GEOGRAPHICAL AND ECOLOGICAL DISTRIBUTION
Nilgai are endemic to peninsular India. Historical records point out that
all the Mughal emperors were extremely fond of hunting nilgai, especially
Jehangir, credited with hunting down, among other animals, nearly 900
nilgai (Ali 1927). In the past, nilgai were distributed in open vegetation
types all over India, down to Mettupalayam (latitude: 11 ° N) in south India
(Brander 1923, Pythian-Adams 1951, Prater 1971). The present
distribution of nilgai ranges from the Himalayan foothills, southward
through central India, down to the southern districts of Andhra Pradesh.
They are found in 114 Protected Areas of the country, in 16 States: Andhra
Pradesh, Bihar, Chattisgarh, Gujarat, Haryana, Himachal Pradesh,
Jammu and Kashmir, Madhya Pradesh, Maharashtra, Orissa, Punjab,
Rajasthan, Uttar Pradesh, Uttaranchal, Jharkhand and West Bengal. They
are absent in the north-east India, and the southernmost parts of the
peninsula. Nilgai have also been reported in Pakistan, mainly along the
border with India (Mirza and Khan 1975, Roberts 1977) and in Nepal
(Dinerstein 1979). Introduced nilgai populations occur in U.S.A., Mexico
and South Africa (Lever 1985).
Nilgai occur near human habitations and crop fields outside protected
areas. They are found in a variety of habitats, from level ground to
undulating hills, in thin brush with scattered trees to cultivated plains,
but not in dense forests and steep hills (Blanford 1888, Prater 1971).
They are absent from the true arid zone where woody cover is inadequate
to meet their requirements.
POPULATION
Though nilgai were once common throughout India (Adams 1858, Blanford
1888), like most large mammalian fauna of India, they have declined
drastically because of habitat destruction and over-hunting (Schaller 1967).
30
UNGULATES OF INDIA
i
Nilgai
Roberts (1977) reported that nilgai numbers are much reduced even in
India, despite being regarded as sacred by the Hindu farming population.
Their current population in India is yet to
be assessed
. Population figures
are rarely available even from within the PAs from where they have been
reported. Needless to say, estimating nilgai numbers outside PAs becomes
even more difficult. However,
a safe estimate
of nilgai in India would be
between 100,000 and 150,000. North-central India, covering four states
(Haryana, Madhya Pradesh, Rajasthan, and Uttar Pradesh) account for a
large majority (about 60%) of the total nilgai population in the country.
ECOLOGY
Group size and composition
Nilgai are partially social in their habits (Roberts 1977), although
congregations and large groups
are rare
. According to Dinerstein (1980),
nilgai occur in groups ranging from one to 10 individuals, and the mean
group size observed in Karnali-Bardia in Nepal was 2.9. In Sariska, seasonal
group size of nilgai (excluding single individuals) varied greatly, from two to
43 individuals, with a mean group size of 4.0 (Sankar 1994), with groups of
up to five individuals formed 87 per cent of the groups observed. In Gir,
Khan
et al.
(1995) reported mean group size of nilgai (including 'groups' of
one) as 2.2, with high seasonal variability in group sizes.
According to Schaller (1967), nilgai groups change constantly, but three
distinct kinds of groups are discernible: (i) one or two cows with young
calves, (ii) 3 to 6 adult and yearling cows with calves, and (iii) male groups
varying in number from 2 to 18. Sheffield
et al.
(1983) reported that in
Texas, nilgai exhibited sexual segregation, except during the breeding
season (December to March), when groups were formed with a male,
and one or more cows and their calves. During the non-breeding season,
especially the monsoon in India (July-October), bulls were usually found
in all-male groups of less than 10 individuals, or sometimes in groups of
10 to 23, rarely more. Non-breeding cows and their calves occur mainly
in groups of less than 16, often as singles and occasionally in larger
groups of 16 to 24. During the breeding and calving seasons, this
structure may change (Sankar 1994).
Sex ratio
Data from captive-bred nilgai indicated that the sex ratio of nilgai at birth
is approximately even. Of the 535 nilgai born in zoos worldwide, 49%
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3
1
were males and 51% females (Jarvis 1968, Lucas 1970). In India, the
sex ratio (male:female) of free ranging adult nilgai favours females: 0.59:1
in Bharatpur (Schaller and Spillett 1966), 0.39:1 in Vanvihar Sanctuary
(Schaller 1967), and 0.4:1 in Sariska (Sankar 1994). In Gir, down the
years, the female-biased sex ratio of nilgai appears to be tilting more
towards females: from 0.89:1 (Berwick and Jordan 1971) to 0.71:1 (Khan
et a!. 1995). In Texas, the observed male:female ratio was 0.81:1
(Sheffield
eta!.
1983).
The female:calf ratios for free-ranging nilgai are: 1:0.23 in Gir (Khan
et
a!. 1995), 1:0.48 in Sariska (Sankar 1994), and 1:1.03 in Texas (Sheffield
et a!. 1983). The higher number of young in nilgai, as compared to
sympatric ungulates, can be attributed to twinning (Kyle 1990, Sankar
1994) and strong defence of calves by cows making them less vulnerable
to predation (Sankar 1994). One adult female nilgai in Sariska was
observed guarding a 'creche' of four calves (A.J.T. Johnsingh pers.
observ.). Of the 755 calves encountered in Sariska, 80 per cent were
twins. The study on free-ranging nilgai in Texas also recorded births of
triplets (Kyle 1990). The main reason for the lower female:fawn ratio in
Texas was due to a combination of twinning and the total absence of any
large
predator there.
Reproduction
According to Prater (1934) and Asdell (1946), nilgai have no regular
rutting season. In central India, Brander (1923) noticed calves of free-
ranging nilgai in all seasons. In Bharatpur, most calves were born during
the rainy season (June to October), and most breeding activity occurred
from October to February, with a peak in November and December
(Schaller 1967). Data from captive nilgai in zoos throughout the world
showed that peak periods of birth last for 3 to 4 months, but these peak
months varied from location to location (Sheffield
eta!.
1983). In Sariska,
though new born nilgai calves were seen from July to November, most
of the calving was observed in October and November (Sankar 1994).
Judging from this fact, and the knowledge that their gestation period is 8
to 9 months (Crandall 1964, Prater 1971), nilgai in Sariska would have a
peak rut from December to January.
Predation and mortality
Predation on nilgai by large predators like tiger (Panthera tigris)
and leopard
(P pardus)
in Rajaji (Johnsingh
et a!.
1993) and in Sariska (Sankar
et al.
32
UNGULATES
OF INDIA
Nilgai
1993) was negligible. The same applied for the lions in Gir (Chellam 1993).
Due to large body sizes and gregarious habits of adult nilgai, leopards
(Panthera pardus)
may find it very diff icult to hunt them down. The preference
of nilgai for human-dominated habitats make them less vulnerable to predation
by tiger. Nilgai cows may be capable of defending their calves from
predators. Sankar (1994) once observed an adult nilgai female with two
young calves chasing away a tiger, and a dhole
(Cuon alpinus)
on another
occasion. Very little information is available on mortality in nilgai other than
natural predation. In Sariska, eight dead nilgai were diagnosed with symptoms
of foot-and-mouth disease (FMD) (Sankar 1994). Nilgai, being an antelope
and therefore less dependent on water, was least affected by the severe
drought of 1988 in Sariska, when, of the 153 wild ungulates killed by the
drought, only 18 were nilgai (Goyal
eta!.
1993).
Food habits
Studies on nilgai food habits showed that they are browsers (Berwick 1974,
Mirza and Khan 1975, Dinerstein 1979,1980) or mixed feeders (Haque 1990,
Sankar 1994). In southern Texas, they are grazers (Sheffield
eta!.
1983).
Nilgai can thrive upon variable proportions of grass, herbs, and browse,
subject only to a minimum requirement of protein, which must not be below
8 per cent of their intake. A study of ungulate food habits in Nepal (Dinerstein
1979) indicated that sambar and nilgai feed on the same browse species.
Apart from this, there is little information available on the dietary overlap
between nilgai and other wild ungulates. According to Rodgers (1988), the
large size of nilgai means they can exist on much poorer quality food items,
making them coarser browsers. They are also fond of raiding crops and are
regarded considered as pests in agriculture fields. Their ability to reach up
to a height of 2.2 m height (bulls) helps in accessing forage in heavily grazed
areas. At times, even female nilgai have been observed standing on hind
legs and feeding on
Zizyphus mauritiana
leaves and fruits (K. Sankar
pers.
observ.).
Nilgai was found associated with common langur
(Semnopithecus
entellus)
in feeding areas in Sariska, gleaning food dropped by them.
In Sariska, nilgai fed on 91 plant species that included 20 tree, nine shrub, 12
creeper/straggler, 29 herb and 21 grass species (Sankar 1994). Grass formed
an important component of nilgai diet during and soon after monsoon. During
winter and summer nilgai fed on fallen leaves and fruits of
Zizyphus mauritiana,
fallen flowers of
Butea monosperma,
fallen pods of
Acacia nilotica, A. catechu
and
A. leucophloea,
and fallen leaves of
Anogeissus pendula,
along with grass
and browse. Like most other mammals, freshly fallen flowers of mahua tree
(Madhuca indica) are a favourite for chital in Central India. Analysis of preference
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NIV
new range about 1.6 km away in an area with ponds (Sheffield
et al.
1983).
BEHAVIOUR
Mating system
D
ring
b d
i
uring the breeding season, the bulls move about in search of breeding
cows, and upon finding one, defend the area around her from intrusions
by other males - a system described as 'roving territoriality' (Sheffield
3 4
ratings and the dietary importance of browse species of nilgai in Sariska revealed
that the leaves
of
Capparis
sepiaria
(
crude protein content
(CPC) = 10 to 14%),
Grewia flavescens
(CPC = 8 to 14%) and
Zizyphus
mauritiana
(CPC = 3.9 to
10.5%) were the preferred plant species
(
Sankar 1994).
Habitat use and home range
Nilgai are found in open areas with undulating or flat terrain (Berwick
1974); they avoid dense hilly forests and prefer scrublands with low tree
and shrub densities (Chakraborty 1991, Sankar 1994, Khan 1996). A
radio-collared nilgai female had a mean seasonal home range of 3.6 km2
in Sariska (Sankar 1994), and its annual home range was 7.3 km2. In
Texas, a nilgai female had a 0.6 km2 home range, and the mean home
range of eight bulls was 4.7 km2 (Sheffield et al.
1983). In India, nilgai
are generally considered diurnal (Brander 1923, Schaller 1967), and the
same holds true for the Texan population, although some degree of
nocturnal activity did occur (Sheffield et al.
1983). In Nepal, Dinerstein
(1979) reported two activity peaks (0700 and 1800 hrs) for nilgai during
summer, and a radio-collared nilgai female in Sariska also showed two
activity peaks, 0700 to 0900 hrs, and 1600 to 1800 hrs during winter
(Chakraborty 1991).
Water use
In Nepal, Dinerstein (1979) observed that the availability of surface water
influenced the distribution and movements of ungulates including nilgai.
According to Prater (1971) nilgai can go for long periods without water,
and even during the hot weather, nilgai do not need to drink water regularly.
Nilgai are reported to be water independent even in desert areas (Bohra et
a/. 1992). A 168 kg nilgai male in Texas drank up to 14 litres every 24
hours during July-August, when temperatures reached 40°C. During a
drought in Texas in 1971, a radio-collared bull deserted a home range
soon after all surface water had evaporated from there, and established a
UNGULATES
OF INDIA
Nilgai
et al.
1983). Mature bulls maintain an area of dominance around
themselves, whether or not cows are present. Breeding bulls respond to
intrusions into these areas from other bulls by displays, threats, and
chases, which either results in the intruding bulls leaving, or remaining
in the area in a subordinate status. Courtship in nilgai is simple and
involves a neck-stretched-forward, tail erect display by the male, showing
the conspicuous white ventral side, and following the female in oestrus
during a slow, sedate mating march.
Vocalisation
Although normally silent, nilgai have several vocalisations. Adults of both
sexes, and calves as young as 5 months of age, sometimes utter a guttural
alarm, more frequently when nilgai detects a hidden motionless observer,
and especially when the wind direction is not in its favour. The call is audible
for a distance of nearly 500 m. The alarm call of cows is of a higher pitch
than that of bulls. Calves also call in a higher pitch, but much more softly.
The alarm call of one group member usually alerts others, which sometimes
join in. A low-pitched belching moan can be heard occasionally when one
bull chases another (Sheffield
et al.
1983). At times, cows produce a very
low-pitched call to their calves (K. Sankar
pers. observ.).
Display behaviour
Adult bulls display their dominance in many ways. A 'head-up' display
consists of a raised muzzle exposing the white throat patch to adversaries.
Another display is the 'horizontal-neck' display, where the head and neck
is held stiff and stretched horizontal with the gular hair tuft and pinnae
completing the picture. A bull would also exhibit a 'lateral display' when
another male challenges him or when walking towards a subordinate.
During the lateral display, the forelegs are held stiff, while the hind legs
are brought forward under the body so that the rump is lowered and the
back prominently arched. The head and neck are stretched forward, ears
are held below horizontal and the male walks with short, slow, and deliberate
steps. Viewed laterally, a displaying male appears massive at the chest
and lower neck and relatively small at the rump. The eyes appear glazed
and are rolled back, exposing the whites (Sheffield
et al.
1983). During
this process, the neck is stretched forward. Remarkably, this lateral display
never occurs when opponents are very close to each other (Sheffield
et
a!. 1983). Sometimes bulls also jerk their head down to point the tip of their
horns to their opponents. Submissive behaviour recorded in Sariska
included that of a sub-adult nilgai bull sitting on its belly with forelegs folded
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35
beneath
,
and repeatedly butted the chin of an adult bull
,
which stood over
it, extending its neck
(A.J.T. Johnsingh
pers. observ.).
Fighting
Walther (1974) described two types of fighting in nilgai bulls: (i) the
combatants stand or kneel, and butt each other on the forehead with
their horns, (ii) a neck-fight, in which both animals either stand or kneel,
and push their necks against each other. Nilgai are the only bovids that
exhibit neck-fighting between horned bulls. However, hornless cows of
several bovids (including nilgai) neck-fight, which Walther (1974)
considered phylogenetically very old, and suggested that it was also part
of the behavioural repertoire of hornless ancestors of the modern horned
ungulates. The persistence of this behaviour in nilgai bulls may relate to
their relatively primitive horn structure. Since these horns are ineffective
binding instruments, the common and more highly evolved head-to-head
shoving with crossed horns (as observed in gazelle and kudu), has not
developed in nilgai.
Calf behaviour
As seen in several species of ungulates, nilgai calves remain hidden for a
while after birth, a habit called `lying out'. Twin nilgai calves born in captivity
spent their first 10 days sleeping inside a shed, and rising only to nurse at
two-hour intervals (Lacey 1969). In Texas, the period of remaining hidden
lying-out was about a month, after which the calves began travelling with
their mother. This transition from lying-out to continued association with
the mother appeared to occur gradually (Sheffield
et al.
1983).
Dung piles
Nilgai have a characteristic habit of defecating repeatedly in the same
location, resulting in the formation of large faecal piles or lavatory sites of
nearly a meter in diameter (Brander 1923, Dharmakumarsinhji 1959, Schaller
1967). The social significance of this phenomenon is not yet clear. Schaller
(1967) suggested that these piles might function as territorial markers, since
the behaviour is characteristic of several species of African antelopes
(Leuthold 1977). Contrastingly, in Texas, there was little evidence that nilgai
were territorial despite using faecal piles (Sheffield
et al.
1983). As evident
from the different sizes of pellet groups at faecal piles, all age- and sex
classes, including calves, use lavatory sites, although bulls undoubtedly
use them more often than cows and calves (K. Sankar pers. observ.).
36
UNGULATES OF INDIA
Nilgai
CONSERVATION
Although there has been a reduction in the overall range of nilgai, the existing
populations seem to be doing fairly well. This is largely because of they are
a protected species under the law, and more importantly the protection they
acquire from being considered sacred due to their resemblance to domestic
cows. Moreover, gradual degradation of dense forests into open scrub and
thickets, increasingly bordered by agricultural fields, has offered favourable
habitat conditions for the increase of nilgai numbers. Invariably, in such
situations, nilgai become serious pests as crop raiders and a major issue of
human-wildlife conflict. Possible solutions voiced include a selective culling
programme linked to licensed hunting permits. However, throughout the range
of the nilgai, most farmers are Hindus, and in Rajasthan and Haryana, many
of them are Bishnois, a sect that rigorously protects all animals. Bishnoi
farmers prefer to tolerate the raids on their crops rather than permit the
slaughter of nilgai. So it is highly unlikely that any scheme to cull or ranch
nilgai either for hunting or for local consumption will ever work in India (Kyle
1990). This attitude may however change, when the number of people living
off the land increases, when the local people begin to believe nilgai are
vermin or a source of meat. Relocations of problematic nilgai, for the time
being, seem the safest solution.
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Nilgai
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40
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... Довжина тіла -у межах 180-210 см у самців і 170 см у самок, обхват грудей 160 і 130 см, довжина голови 46 і 43 см, довжина хвоста 46-53 і 45 см, довжина вух 15-18 і 15 см відповідно, висота в холці 120-140 см у самців і самок, висота в крижах 110 см у самців і самок (The fauna …, 1888; Sheffield, Fall, Brown, 1983). Лише самці нільгау мають міцні, конічні та гладенькі роги довжиною 15-24 см (The fauna …, 1888; Schaller, 1967;Sheffield, Fall, Brown, 1983;Sankar, Johnsingh, Acharya, 2004). ...
... Така поведінка характерна також для кількох видів африканських антилоп. Нільгау всіх статево-вікових категорій використовують такі майданчики (Sankar, Johnsingh, Acharya, 2004). В Асканії-Нова при утриманні в загонах нільгау також випорожнювалися у певних місцях. ...
... Підгодівля гілковим кормом є обмеженою, хоча нільгау з задоволенням їдять листя і молоді пагони. В природі самки можуть ставати на задні ноги, щоб дістати листя дерев і фрукти (Sankar, Johnsingh, Acharya, 2004). У вольєрі екскурсійного маршруту зоопарку "Асканія-Нова" молоді самець і самка також балансували на задніх кінцівках, поїдаючи листя шовковиці білої, яка росте поряд з огорожею, дорослі тварини цього не робили. ...
Article
Викладено результати досліджень розведення нільгау в зоопарку "Асканія-Нова". Виділено три періоди розведення, надано характеристику завезених антилоп. Наведено динаміку чисельності, вибуття і народжуваності тварин протягом другого і третього періодів розведення (1948–2023 роки). Описано умови утримання і причини формування груп нільгау. Охарактеризовано особливості розмноження цього екзотичного виду антилоп в умовах півдня України. У нільгау спостерігається сезонність розмноження, хоча самки здатні народжувати упродовж року. Абсолютна більшість телят нільгау народилася з січня по травень, з піком у лютому–квітні. Співвідношення самці : самки у новонароджених становило 1,14 : 1. Збереженість молодняку в зоопарку "Асканія-Нова" від народження до 6-місячного віку складала 57,7%, до 12-місячного – 51,3%. Вагітність тривала 243,8±0,57 днів. Плодючість самок нільгау в зоопарку "Асканія-Нова" в середньому становила 80,1%. Самки народжували телят до 13–14-річного віку. Вага новонароджених самців становила 6,35±0,32 кг, або 2,31% ваги дорослого (235,0±5,7 кг), вага новонародженої самки складала 5,8±0,4 кг, або 3,5% ваги дорослої тварини (165,1±3,3 кг). У річному віці вага самців і самок становила 50,5 і 69,6% ваги дорослих тварин, дворічному – 69,0 та 93,9% відповідно. Показники екстерʹєру і ваги у дорослих тварин знаходилися у межах норми, характерної для даного виду. Так, висота в холці у самців і самок складала 131,0±1,0 і 122,3±1,1 см, коса довжина тулуба 130,0±1,5 і 144,7±2,1 см, обхват грудей 158,8±1,0 і 144,7±2,1 см, обхват грудей 61,2±0,7 і 55,5±0,8 см відповідно. Охарактеризовано етологічні особливості нільгау при утриманні у неволі. Описано результати полівидового утримання нільгау з представниками родин Конячих, Оленячих, Порожнисторогих. В період розмноження антилоп бажано утримувати окремо від Конячих. Припустимим є їх спільне знаходження у великих загонах з густою рослинністю. Наведено рекомендації з покращення утримання нільгау у зоопарку "Асканія-Нова".
... They are found in a variety of habitats from level ground to undulating hills, in thin bush with scattered trees to cultivated plains, but not in dense forests and steep hills (Blanford, 1888;Prater, 1971). They are absent from the true arid zone where woody cover is inadequate to meet their requirements (Sankar et al., 2004). Gradual degradation of dense forests into open scrub and thickets, increasingly bordered by agricultural fields, has offered favourable habitat conditions for the increase of Nilgai numbers and they hence are seen often in human or agricultural landscapes (Sankar et al., 2004). ...
... They are absent from the true arid zone where woody cover is inadequate to meet their requirements (Sankar et al., 2004). Gradual degradation of dense forests into open scrub and thickets, increasingly bordered by agricultural fields, has offered favourable habitat conditions for the increase of Nilgai numbers and they hence are seen often in human or agricultural landscapes (Sankar et al., 2004). ...
... The crude protein content of the identified plant species in the diet of Nilgai fell in the range between 2.47% to 23.01%. Nilgai can thrive upon variable proportions of grass, herbs, and browse, subject only to a minimum requirement of protein, which must not be below eight per cent of their intake (Sankar et al., 2004). The crude protein content in the plant species occurring more frequently in the pellets of Nilgai had a crude protein content of more than eight percent except Zizyphus nummularia fruits (7.60%) but this too did not deviate much from the threshold value of eight percent as proposed by Sankar et al. (2004). ...
Article
Full-text available
We examined the food habits of the Nilgai (Boselaphus tragocamelus) from May 2012 to September 2013 in a human dominated central Saurashtra landscape using microhistological technique of pellet samples. A total of 112 pellet samples were collected over three seasons- summer, monsoon and winter and analyzed for percent frequency of occurrence of different plant species. Contribution to the diet by monocots and dicots showed seasonal differences (ANOVA, F= 6.45, df=15, p=0.011) and the Nilgai was found to be a mix feeder through all the seasons in the study area.
... Kafle et al. (2020) have reported open grazing as high threat and invasive species as the low threat to wild animals in Laljhadi Mohana Biological corridor (LMBC); but our study has shown that open grazing and invasive species are the foremost conspicuous threat to blue bulls in BNP. The pressure of livestock and establishment of invasive species has degraded the suitable habitat of blue bulls by limiting the quality and quantity of vegetation inside the forest as blue bulls require more nutritious diet (Sankar et al., 2004). With this situation of lack of sufficient food resources inside the park area (Khatri, 1993), people claimed that blue bulls usually visit their agricultural fields and damage huge area of cultivated land by trampling and consuming crops. ...
... Aryal, M., Panthi, S., Bhatta, M., Magrati, T. P., Shrestha, A. K., Shrestha, P. B. and Karki, A. 2016 Chhetri, N. B., Dhami, B., Neupane, B., Sadadev, B. M. and Thapa, N. 2020 Kafle, K., Thanet, D. R., Poudel, P., Gautam, D., Thapa, G. and Bhatt, P. 2020 , 18:455-465.http://dx.doi. org/10.1111/j.1523-1739.2004.00483.x Mallon, D.P. 2008. ...
Article
Full-text available
Blue bull is Asia’s largest antelope, a species of least concern in IUCN Red data list of 2020. In Nepal, it is vulnerable and is often considered as a problem animal for its crop raiding habit. Although, its population is restricted in India and Nepal, there are insufficient studies conducted on the distribution and threats of the species at local level. This study aimed to assess the distribution of blue bull and its conservation threats in Bardia National Park and its buffer zone. Field survey was carried out to identify the potential area with the information provided by park staff and buffer zone people and by the transect method in the selected habitat to determine the distribution of blue bull population. Additionally, six focus group discussions (1 in each of thefive sites and 1 with park staff) and a half-day workshop (involving 25 participants representing each site and park office) were organized to assess the existing threats to the species. Data were analyzed descriptively using MS Excel, while the distribution map was prepared using Arc GIS. Also, 8 major identified threats were ranked using relative threat ranking procedure and classified into four severity classes. We found that the population of blue bull was dispersed from core area of Bardia National Park towards the buffer zone area. Open grazing, invasive species, predation by tiger and flash flood were the major threats to the blue bull as perceived by the local people. Habitat management activities including control of grazing, removal of invasive plant species, plantation of palatable grass species, increase in other prey species of tiger and control of flood in blue bull’s habitats are recommended to protect the species and thus sustain their threatened population.
... Nilgai habitat in South Texas grasslands is similar to their native range in India. In India, nilgai generally avoid dense forest and prefer level or undulating plains covered with grass and patches of scrubs (Sankar et al., 2004) which is characteristic of the South Texas plains. In India, there are also several large predators including tigers, (Panthera tigris); lions, (Panthera leo); leopards, (Panthera pardus); wolves, (Canis lupus); and striped hyenas, (Hyaena hyaena); that effect their survival, reproduction and behavior. ...
Article
Full-text available
Cattle fever ticks (CFT), vectors of bovine babesiosis and anaplasmosis, were eradicated from the United States by 1943, but are frequently reintroduced from neighboring border states of Mexico via stray cattle and wildlife hosts including white-tailed deer (Odocoileus virginianus) (WTD) and nilgai antelope (Boselaphus tragocamelus). Nilgai antelope are exotic bovids from India that are hosts of CFT, have large home ranges as compared to WTD, thus have the potential to spread CFT through the landscape. Currently, there are no methods to control CFT on nilgai. Odor lures were evaluated to determine if nilgai could be attracted to a central point for development of control methods. Four treatments, nilgai offal a natural odor lure was used as the positive control; and compared to three artificial odors; screw worm lure, volatile fatty acids, citronella oil. Studies were conducted on a free-ranging population of nilgai at the East Foundation's Santa Rosa Ranch (Kenedy Co., near Riviera, Texas, USA). Game cameras were used to document visitation to the lures. In the ten randomly placed transects, 110 nilgai and 104 WTD were photographed. Offal had significantly more visits by nilgai (71% of total visits) than screwworm (15%), VFA (11%), and citronella (4%). For WTD, there was no significant difference in visitation at the lure treatments.
... In most sexually dimorphic mammals, colour patterns vary little within the sexes (e.g. Caro 2005;2013), exceptions being the blue bull Boselaphus tragocamelus (Sankar et al. 2004), the common eland Tragelaphus oryx (Hillman 1987), the African lion Panthera leo (West and Packer 2002), as well as hair and skin colour in several primate species (e.g. Schaller 1963;Gerald 2001;Setchell et al. 2008;Bergman et al. 2009). ...
Article
Full-text available
Coexistence of individuals within a social group is possible through the establishment of a hierarchy. Social dominance is achieved through aggressive interactions, and, in wild sheep and goats, it is related mainly to age, body size and weapon size as rank signals. Adult male Himalayan tahr are much larger than females and subadult males. They have a prominent neck ruff, ranging in colour from yellow (5.5-9.5 years old, i.e. young adults, golden males) to brown (7.5-14.5 years old, i.e. older individuals, pale and dark brown males), with golden males being the most dominant. We investigated the social behaviour of male tahr and analysed the relationships between ruff colour, courtship and agonistic behaviour patterns during the rut. Colour classes varied in their use of several behaviour patterns (male dominance: approach, stare, horning vegetation; courtship: low stretch, naso-genital contact, rush). Golden-ruffed males used more threats than darker ones. Pale brown and dark brown males addressed threats significantly more often to males of lower or their own colour classes, respectively, whereas golden ones addressed threats to all colour classes, including their own. The courtship of dominant males was characterised by the assertive rush, whereas that of subordinates did not. Ruff colour of male Himalayan tahr may have evolved as a rank signal, homologous to horn size in wild sheep and goats.
... It is generally classified as intermediate feeder, seasonally including considerable amounts of browse such as Acacia and other trees in its diet (Schaller, 1967). Its food choice in its Asian habitat is described as including grass, but being clearly dominated by browse (Dinerstein, 1979; Khan, 1994; Sankar et al., 2004); free-ranging animals in Texas display higher proportions of grass but are still clearly identified as intermediate feeders (Sheffield, 1983), a classification that was also confirmed in experimental feeding plots in India (Solanki and Naik, 1998). In consequence, a lower SF RR was expected for nilgai compared to blackbuck. ...
Article
Digesta retention patterns have been suggested to play a major role in ruminant diversification. Two major digestion types have been proposed, termed 'cattle-type' and 'moose-type', that broadly correspond to the feeding categories of grazers and intermediate feeders on the one, and browsers on the other hand. We measured and calculated the mean retention time (MRT) of a solute and a particle (<2mm) marker in the gastrointestinal tract (GIT) and the reticulorumen (RR) of a small grazer, the Indian blackbuck (Antilope cervicapra, n=5, body mass 26±4kg) and an intermediate feeder, the nilgai (Tragocamelus buselaphus, n=5, body mass 168±21kg). MRTsolute and MRTparticle were 29±4.1h and 60±6.6h in blackbuck and 28±2.5h and 54±8.9h in the nilgai for the GIT, and 14±1.7h, 45±5.0h, 19±2.0h and 45±8.4h for the RR, respectively. With a selectivity factor (SF, the ratio of MRTparticle to MRTsolute) in the RR of 3.2±0.28 for blackbuck and 2.3±0.36 for nilgai, both species are clearly in the category of 'cattle-type' ruminants. In particular, the high SFRR of blackbuck, in spite of its small body size, is remarkable, and leads to specific predictions on the RR anatomy of this species (such as a particularly large omasum), which can be tested in further studies. The adaptive value of a high SFRR is mainly considered as an increase in microbial productivity in the RR; exemplary estimations based on the measured passage rates of solutes indicate an 8% higher production of microbial mass in blackbuck compared to nilgai. Copyright © 2014. Published by Elsevier Inc.
... Changes of coat colour may also depend on physiological maturation (e.g. Sankar et al., 2004, for the blue bull Boselaphus tragocamelus; Hillman, 1987, for the common eland Tragelaphus oryx, where adult males are either grey or brown, with the "grey males always dominant over brown"), but relevant information is scarce (Caro, 2005). In mammals, changes of coat colours are usually related to ageing rather than to dominance and/or mating success (Caro, 2005), whereas in birds plumage colour is often related to social status (e.g. ...
Article
Full-text available
In ungulates, rank order is determined by differences in weight, body size, weapon size and age. In the Caprini tribe (Bovidae: Caprinae), adult male Himalayan tahr are unique to show different coat colours, but no sexual dimorphism in weapons. A highly significant correlation between hair colour and rank order was found during the rut: males with a lighter coloured ruff dominated over darker ruffed ones, in both aggressive interactions and access to oestrus females. We studied colour-based dominance in relation to weight, age and testosterone levels, which establish the social rank in most ungulates. No differences in weight and testosterone concentrations were found between adult male colour classes, but males with paler ruffs were significantly younger than darker adult males. The distribution of physical traumas from fights confirmed that younger, lighter-coloured males had a higher rank than older, darker males, a pattern which is unusual amongst ungulates. Coat colour seems to work as a signal of rank in male–male aggressive interactions and it changes according to age, whereas the relevant physiological determinants deserve further research. Intrasexual male competition has not changed weapon size or shape in the Himalayan tahr, but ruff colours are apparently used to signal rank and dominance. Colour patterns of adult males may then be homologous to ritualised weapons, apparently being a unique feature of male tahr amongst mammals.
Chapter
Full-text available
This chapter portrays Rajasthan as home to nine species of wild ungulates, including the four of antelopes and five species of deer. Deer and antelopes are protected by the Indian Wildlife (Protection) Amendment Act, 2006 under Schedule I and Schedule III. Out of a total of six species of antelopes found in India, the four are present in Rajasthan, namely, Nilgai Boselaphus tragocamelus, Four-horned Antelope Tetracerus quadricornis, Indian gazelle or Chinkara Gazella bennettii, and Blackbuck Antilope cervicapra. Distribution range and pattern of each species has been described in detail. The significance of these beautiful creatures as herbivores and the major prey base for wild carnivores has been highlighted in addition to their aesthetic value. Nilgai has come in confrontation with locals as crop pest in the recent years, whereas in some areas, Blackbuck also cause damage. Indian gazelle, however, is in complete harmony with locals. The chapter also discusses the magnificent deer of the state which are distributed largely in protected areas of northeastern Rajasthan and the Aravallis. Sambar Rusa unicolor and Chital Axis axis are quite common in Rajasthan, while the Hog Deer Axis porcinus and Southern Red Muntjac or Barking Deer Muntiacus muntjak are confined to Keoladeo National Park. Mouse Deer are limited to only one district in southern Rajasthan. The need for further detailed study regarding their population estimates and conservation has been taken into consideration in this chapter.
Article
The habitat occupance and factors governing the distribution of major ungulate species were investigated in Gir Lion Sanctuary from January 1988 to March 1989. Direct sightings and sampling of pellet groups of ungulates on eight line transects, each six km long ,were used to calculate seasonal habitat preference index and to assess the effect of 19 habitat variables on pellet group densities using multiple regression analysis. The habitat preference index for chital varied seasonally among different habitat types and was significantly correlated with pellet group density of chital in different habitats. The measured habitat variables explained only a maximum of 50%, 57% and 32% of variation in pellet group densities of chital [Axis axis (Erxleben)], sambar [Cervus unicolor (Kerr)] and nilgai [Boselaphus tragocamelus (Pallas)] respectively. The mean pellet group density for each species differed significantly among the habitats. The overall pattern of habitat occupance remained same between the years for all ungulate species.
Article
The habitat utilisation by ungulates in a newly created tiger sanctuary of the southwestern Nepalese Terai is analysed. While most of the Royal Karnali-Bardia Wildlife Reserve is covered by a rather homogeneous belt of moist subtropical deciduous forest, one section of the reserve supported a wide variety of habitat types. In this area, flood plain, savannah, and several riverine forest associations intergraded with stands of the dominant Shorea robusta forest. Free-living mammals responded to this ecological heterogeneity, permitting an analysis of habitat preferences by the following species: chital Axis axis, nilgai Boselaphus tragocamelus, hog deer Axis porcinus, barking deer Muntiacus muntjak, swamp deer Cervus duvauceli, sambar Cervus unicolor, and two primate species, common langur Presbytis entellus, and rhesus monkeys Macaca mulatta. Differences in feeding and anti-predator strategies offered a degree of ecological separation between most of the ungulates studied. Changes in plant distribution and phenology affected ungulate food habits, energy budgets, movements, and seasonal distribution. A special feeding relationship between certain ungulates and langur and rhesus monkeys was observed. The sambar, an ungulate capable of exploiting a feeding niche in continuous climax forest, appears to be best adapted to the habitat types which dominate most of Karnali-Bardia, while only 30% of the reserve could be considered prime habitat for the chital, the most abundant grazing ungulate in the reserve. Proposals to improve habitat conditions for grazing ungulates through an experimental programme integrating controlled burns, water hole development, and the creation of openings in continuous climax forest are examined.
Article
Population density and biomass estimates for wild and domestic ungulates in the Royal Karnali-Bardia Wildlife Reserve, Nepal, are presented and compared with values obtained from other reserves in South Asia. Wild ungulate population densities varied in relation to habitat diversity; large herbivores were most numerous where early and intermediate successional stages intergraded with one another and only sparsely distributed in continuous climax sal Shorea robusta forest. Chital Axis axis was the most abundant wild ruminant in the reserve. It and the nilgai Boselaphus trago-camelus constituted 88% of the total wild herbivore biomass in the southwestern corner of Karnali-Bardia, where an intensive study was carried out. The biomass of domestic stock utilising the same study area in 1975 was computed to be 15–17 times higher than the levels attained by wild ungulates in April of 1977, nearly two years after the reserve borders had been closed to domestic grazing. Observations during the hot-dry season indicated that both wild and domestic ruminants competed for the same forage species.Among the wild ungulates, chital were decidedly the most gregarious, commonly associating in feeding aggregations of over 20 individuals on the open savannahs. Nilgai and wild boar Sus scrofa formed smaller groups while barking deer Muntiacus muntjak and hog deer Axis porcinus were primarily solitary. Chital exhibited a peak in rutting activity during the late hot-dry season and a subsequent birth peak in February. Nilgai exhibited a different pattern, breeding in January and calving during the monsoon, when optimum foraging conditions prevailed.