Overview

Brief Summary

Biology

A solitary animal (2), the Bawean deer is usually only seen with another deer if it is a mother and her young, a courting pair, or two rival males fighting over a female (4). When with another individual, the Bawean deer can be heard communicating with short, sharp, barks (4). Although capable of breeding at any time of the year, Bawean deer mate primarily between July and November. After a gestation period of around seven months, the majority of young are born between February and June (4). With a preference for grazing (2), the Bawean deer feeds chiefly on forbs and grass-like plants (4). Occasionally, it may also feed on crops (7).
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Comprehensive Description

Description

This rare deer, which exists on only one island, is a short-legged and bushy-tailed species (2). Its coarse hair is uniformly brown in adults, except for lighter patches on the throat and around the eyes (2) (4). Young Bawean deer, or fawns, occasionally have a few faint spots on their coat, but these disappear quickly with age (2). Like other deer, the males of this species are distinguished by their antlers: bony, hornlike growths that are typically shed and re-grown each year (5). The antlers of the Bawean deer, which are fully developed by the age of 21 months, are relatively small compared to other deer living in tropical areas (6).
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Distribution

Range Description

This species is endemic to Bawean Island (= Pulau Bawean), in the Javan Sea off the northern coast of Java, Indonesia (Lachenmeier and Melisch 1996; Grubb 2005). Two main parts of the island are used, the central mountain range, and Mount Bulu in the south-west (Blouch and Atmosoedirdjo 1978, 1987). Tanjung Cina (= Cina Cape), an area of 950 m x 300 m, which has hilly topography in its centre and no resident human population, lies at the north-west of Bawean Island and is often cut off from the main island by a sea level of 20–150 m; it has been much used by Bawean Deer since at least the 1990s (Semiadi 2004).

Today’s restriction to Bawean is a relict from occurrence on Java, probably into the Holocene (van den Brink 1982), its disappearance from Java perhaps being caused by competition with Javan Rusa Rusa timorensis and Southern Red Muntjac Muntiacus muntjak (Meijaard and Groves 2004).

A specimen in the Institute of Zoology, Beijing, is labelled from Bangka Island, which lies off Sumatra (Indonesia); this is presumably in error (Grubb 2005). The species was supposedly discovered by Salomon Müller in 1836 in Tuban, a small town on the northern coast of Java, where the local governor kept a small herd in his garden, and the native range was discovered only after the name was proposed (Sitwell 1970). The species presumably evolved from a Pleistocene Javan Axis species (perhaps Axis lydekkeri) at a time when Bawean was connected to Java via a land bridge (Blouch and Atmosoedirdjo 1987; Meijaard and Groves 2004). Suggestions that the genus was introduced to Bawean by early European settlers seem unlikely (Sitwell 1970) because of the wealth of fossil material (reviewed in Meijaard and Groves 2004), and were not ever referred to by Grubb (2005).
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Historic Range:
Indonesia

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Range

This small deer occurs only on Bawean Island, Indonesia, where it is most abundant in the hilly central region (7). Bawean Island, situated near Borneo, covers just 220 square kilometres (2).
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
Bawean Deer is found in primary and secondary forest, reaching higher densities in the latter (Blouch and Atmosoedirdjo 1978; G. Semiadi and S. Pudyatmoko pers. comm. 2006). The species occurs up to 500 m asl (G. Semiadi and S. Pudyatmoko
Bawean Deer primarily grazes on herbs and grasses, but also browses young leaves and twigs (Blouch and Atmosoedirdjo 1987). An individual deer produces 13 faecal pellet groups per day, a number which has been used to estimate population numbers (Blouch and Atmosoedirdjo 1978). The seasonal rut is in September and October, although males may be found in breeding condition (i.e. with hard antlers) throughout the year (Blouch and Atmosoedirdjo 1987; Whitehead 1993). The gestation period is 225–230 days, after which a single fawn is born, very rarely twins (Blouch and Atmosoedirdjo 1987; Whitehead 1993). Most births occur from February to June; they occasionally occur in other months (Blouch and Atmosoedirdjo 1987). In captivity, breeding occurs year round with females maintaining an interbirth interval of 9 months (Blouch and Atmosoedirdjo 1978).

Bawean Deer are primarily nocturnal, active intermittently through the night. They are very wary, and appear to avoid contact with people; where human activity is heavy, the deer spend the day in forests on steep slopes that are inaccessible to teak loggers. Individuals are occasionally seen on the beach in the southwest of the island, but otherwise are rarely seen directly (Blouch and Atmosoedirdjo 1978, 1987). It is typically solitary, although duos made up of a doe and fawn or a buck following a doe sometimes occur (Blouch and Atmosoedirdjo 1978).

Systems
  • Terrestrial
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Habitat

The Bawean deer inhabits hill forest (2).
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Life History and Behavior

Life Expectancy

Lifespan, longevity, and ageing

Maximum longevity: 17.8 years (captivity) Observations: One specimen lived 17.8 years in captivity (Richard Weigl 2005). Similar species live over 20 years, so it is possible that maximum longevity is slightly underestimated in these animals.
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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
CR
Critically Endangered

Red List Criteria
C2a(ii)

Version
3.1

Year Assessed
2008

Assessor/s
Semiadi, G., Pudyatmoko, S., Duckworth, J.W. & Timmins, R.J.

Reviewer/s
Black, P.A. & Gonzalez, S. (Deer Red List Authority)

Contributor/s

Justification
This species is listed as Critically Endangered because its population size is estimated to number fewer than 250 mature individuals, with at least 90% confined to one subpopulation, which, although currently stable, is expected to go into continuing decline due to an deterioration in habitat quality through invasion by Eupatorium.

History
  • 1996
    Endangered
  • 1994
    Endangered
    (Groombridge 1994)
  • 1990
    Rare
    (IUCN 1990)
  • 1988
    Rare
    (IUCN Conservation Monitoring Centre 1988)
  • 1986
    Rare
    (IUCN Conservation Monitoring Centre 1986)
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Current Listing Status Summary

Status: Endangered
Date Listed: 06/02/1970
Lead Region: Foreign (Region 10) 
Where Listed:


Population detail:

Population location: entire
Listing status: E

For most current information and documents related to the conservation status and management of Axis kuhlii, see its USFWS Species Profile

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Status

Classified as Critically Endangered (CR) on the IUCN Red List (1) and listed on Appendix I of CITES (3).
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Population

Population
Bawean Deer was reported as 'plentiful' during the 19th century. The population increased in the 1950s in response to forest protection, declined during the 1960s–1970s (Grimwood 1976), although no estimates are available, and in the 1980s was thought to number around 300 animals and to be increasing once again (Blouch 1980; Blouch and Atmosoedirdjo 1987). Through a 1991 survey the deer was suspected to be in decline (Gunawan and Kustanto 1994) In 2006, the wild population was estimated (based on field-work in 1998–2003) to be stable at 250–300 animals (Semiadi 2004; G. Semiadi and S. Pudyatmoko pers. comm. 2006), but there has been no systematic survey; 500 would be an absolute maximum (G. Semiadi pers. comm. 2008). Secondary forest seems to be the ideal habitat, supporting up to 19.2 deer per km² (Blouch and Atmosoedirdjo 1978). Teak Tectona grandis forests with understorey, primary forest, and areas with teak and lalang support densities of 3.3 to 7.4 deer per km², while regions dominated by Melastoma polyanthum and Eurya nitida brush, Rombok Merremia peltata, disturbed primary forest, and teak without understorey support only 0.9-2.2 deer per km² (Blouch and Atmosoedirdjo 1987). The most recent assessment is in Semiadi (2004), who drew attention to the wet-season densities of 11.8 animals per km² on Tanjung Cina (= Cina Cape).

Population Trend
Stable
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Threats

Threats

Major Threats
Bawean Deer has been subject to uncontrolled hunting, probably since human settlement took place some 500 years ago. During the 1960s much forest on Bawean was replaced by teak plantations; coupled with increased hunting pressure, this probably caused the species to decline in numbers. Hunting ceased in 1977, and the population increased during the next few years (Anonymous 1978; Blouch and Sumaryoto 1987; G. Semiadi pers. comm. 2006). The hunting of pigs Sus scrofa with dogs persists, and leads to inadvertent death of deer (G. Semiadi pers. comm. 2006), but at the population level hunting is no longer a threat (G. Semiadi pers. comm. 2008). Presently, fewer than five deer die per year through direct human influence, chiefly in traffic accidents and when being chased by local dogs during pig hunts (G. Semiadi pers. comm. 2008). Maturation of teak (including coppicing from cut stumps) and invasion by the American herb Eupatorium odoratum (= Chromolaena odorata; Compositae) constitute the only significant predictable threat to this deer, through reducing the grazing areas and this carrying capacity (G. Semiadi pers. comm. 2008). For a population at best on the edge of the oft-quoted, though somewhat arbitrary, minimum figure for a population viable into the long term (500), such a further reduction (on top of the major contraction in available habitat for the species over past centuries) should be seen as a major threat despite recent population stability.
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Threats

In the past, this diminutive deer was hunted by local people for its meat. Hunting was particularly rampant during the 1960s, when large areas of forest were cut down to plant teak, affording hunters easier access (7). Around 1977, hunting of the Bawean deer diminished, giving populations the respite they needed to recover slightly (7). Today, hunting may remain a contributing factor to the Bawean deer's threatened status, but wild dogs (2), which prey on deer (8), as well as habitat degradation (1) (8), also jeopardise this species' continued existence. Habitat degradation takes the form of the cutting down of trees, the deliberate burning of vegetation, and the encroachment of cultivation by the human inhabitants of the island (9).
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Management

Conservation Actions

Conservation Actions
This species is listed on CITES Appendix I (CITES 2000). It is protected from hunting not just on paper, but effectively in practice (G. Semiadi pers. comm. 2008). It inhabits Bawean Island Nature Reserve (5,000 ha; the island is 200 km² in size), established in 1979 for which a management plan prepared in 1979 (WWF 1979; Blouch and Sumaryoto 1987) warrants revision. Management activities have included termination of hunting, controlled burning of grassy areas within forests, and thinning of teak plantations to encourage understory development (Blouch and Sumaryoto 1987). Since 2000 a captive breeding programme has been operative on Bawean; as of 2006 it involved two stags and five hinds, while about 300–350 animals are held in zoos and private captive breeding facilities off the island (G. Semiadi pers. comm. 2006).

Recommended conservation actions, which should proceed through appropriate revisions to the management plan, include:

1) Increase the populations and if possible expand the area used by the deer. While the population seems to be stable, its small size and insular nature leave it susceptible to chance events (e.g. weather-related disasters or earthquakes or disease), to any resumption of hunting and probably to inbreeding. Increasing Eupatorium will result in time in population decrease. There is thus a major role for active management of habitat through control of Eupatorium, so as to increase population density within the protected area, and thus total population. This species, a problem plant throughout much of South and South-east Asia, is very difficult to control and review of international successes and failures is needed to inform management of the weed on Bawean. Full security would come only through an increase of the range on the island, requiring some deer-centred management for areas outside the protected area.

2) Assess the impact of deer on crops as this may have become a problem if effective protection has allowed the population to increase substantially, or the invasion of Eupatorium is pushing deer to eat more crops. If so, community-based mediation with local conservation officials may be required to find solutions and mitigate conflict.

3) Initiate a co-ordinated breeding programme to evaluate and if necessary address possible inbreeding deficiencies in the captive population.
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Conservation

In 1979, the Bawean Island Nature Reserve was established (7), offering the mountainous habitat of the Bawean deer some much needed protection. Management activities on the island have included protecting the deer from hunting, the controlled burning of grasslands to provide deer habitat, and the thinning of teak plantations to encourage understorey development on which the deer can browse (7) (9). The removal of wild dogs has also been recommended (9). A number of Bawean deer also occur in zoos around the world (4), acting as a safeguard against this species extinction should the worst happen on Bawean Island.
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Wikipedia

Bawean Deer

The Bawean deer, Axis kuhlii, also known as Kuhl's hog deer or Bawean hog deer, is a highly threatened species of deer found only in the island of Bawean (Gresik Regency) in Indonesia.

A typical height for males of 60–70cm has been reported. Males have three-tined antlers.

A Bawean deer.

Their fawns are spotted at birth, which separates them from the best known western population of the hog deer (H. porcinus).


Due to ongoing habitat loss, small population size and limited range, the Bawean deer is evaluated as critically endangered on the IUCN Red List of Threatened Species. It is listed on Appendix I of CITES. It has few natural enemies except for birds of prey and large snakes such as pythons.

Contents

Life History

Bawean Deer Axis kuhlii resides on the Bawean island in Indonesia which is close to the Java Sea. The Bawean Deer is sometimes included with the Hog Deer Axis porcinus (Haltenorth 1963), but it is a total different species (Groves and Grubb 1987; Grubb 2005). The most recent analyses indicate that these two species, together with calamianensis, constitute a different genus distinct from Axis, and Hyelaphus (Meijaard and Groves 2004, Pitra et al. 2004).[2]

They live in woodlands and upland forests with dense undergrowth which is used for shelter, providing a refuge in which the deer sleep and rest during the day. They live in small groups of 4 or 5 deer mostly 1 female, the infant, and 2 males. They are herbivores and consume grasses, herbs, leaves, twigs, corn crops, and leaves of the cassave plants. Their pelage is short, smooth, and soft, and generally a light brown in color. There are few distinctive yellow markings which are limited to the head and neck, there is also a light throat patch or 'bib' and a whitish eye-ring, infants have white spots on their backs when younger. Females will have 1 offspring at a time per year. The gestation period is 225-230 days, and the majority of births occur in February to June.

Males can be very aggressive towards other males that approach their small families, and will spray other males, and predators in the face with their glandular secretions, but also mark their territories with this as well.[3] Also When fleeing the bawean deer carries its head low and runs with a trotting gait. Their spine also curves high towards the rear when fleeing from predators. When fleeing from predators the males will run in front and infant if there is one will be behind the males, and the female will run in the back. This is effective in order to protect the infant from predators. [4]

Conservation Threats

Their past extinction was due to tigers precisely the Balinese Tiger, and humans hunting them for their antlers and pelts. Their main predators now are still humans, but also leopards, the golden jackal, dholes which is the Asiatic Wild Dog, the Indian wolf, pythons, and crocodiles.

Another reason for population decline is from habitat deterioration to build bigger cities, and more places to live and build crops.

Conservation Efforts

The World Wildlife Fund, has said that one of the factors for the reason of the declining of this species, as well as other species found in Indonesia is from climate changes such as warming ocean temperatures, rising sea levels, prolong droughts, and increased flooding. [5] The current conservation efforts which is being done is the Government of Indonesia has the Bawean Deer protected against being hunted which was passed in 1977. With the help of this law that has been passed the reproductive success has gone up over the years. [6] International Union for Conservation of Nature (IUCN) has listed the Kuhl’s hog deer as being Critically Endangered, meaning that the species is facing an extremely high risk of extinction in the wild.[7]

References

  1. ^ Semiadi, G., Pudyatmoko, S., Duckworth, J.W. & Timmins, R.J. (2008). Axis kuhlii. In: IUCN 2008. IUCN Red List of Threatened Species. Downloaded on 8 April 2009. Database entry includes a brief justification of why this species is of critically endangered.
  2. ^ http://www.iucnredlist.org/apps/redlist/details/2447/0
  3. ^ Regional Office of Endangered Species, Eastside Fed. Complex, 911 NE 11th Ave. Portland Oregan 97232, http;//www.pacific.fws.gov
  4. ^ Edinburgh Zoo and Highland Wildlife Park The Royal Zoological Society of Scotland Edinburgh, Scotland, United Kingdom, EH12 6TES
  5. ^ http://www.worldwildlife.org/home-full.html
  6. ^ http://www.edinburghzoo.org.uk/animals/individuals/KuhlsHogDeer.html
  7. ^ http://www.iucnredlist.org/apps/redlist/details/2447/0
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