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| Subspecies: | Unknown |
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| Est. World Population: | |
| CITES Status: | NOT LISTED |
| IUCN Status: | Near Threatened |
| U.S. ESA Status: | NOT LISTED |
| Body Length: | |
| Tail Length: | |
| Shoulder Height: | |
| Weight: | |
| Top Speed: | |
| Jumping Ability: | (Horizontal) |
| Life Span: | in the Wild |
| Life Span: | in Captivity |
| Sexual Maturity: | (Females) |
| Sexual Maturity: | (Males) |
| Litter Size: | |
| Gestation Period: | |
Sus celebensis is an omnivore, with a wide-ranging diet reported (National Research Council 1983, Mustari 2005). They forage during the day, this activity being concentrated in the early morning and evening. Although roots, fallen fruit, leaves and young shoots constitute the bulk of their diet, invertebrates, small vertebrates and carrion are also eaten (Mustari et al. in prep).
There is little known about reproduction of S. celebensis. A pregnant sow reported from south Sulawesi by Sody (1941) was probably mated in February. Births can occur at any time throughout the year but sows usually have their young in April or May (National Research Council 1983). Gestation length is not known for certain, and the suggestion that it may lie between 16 and 20 weeks should be treated with the caution implied by Sody (1941). Litter size ranges from 2-8 (National research Council 1983), but a recent study in North Sulawesi found six pregnant sows killed by hunters to be carrying only 1-3 fetuses with a mean of only 2.17 fetuses per pregnancy (Budiarso et al. 1991).
Sus celebensis is still found in abundance in central, east and south-east Sulawesi. Available evidence suggests that the species formerly occurred throughout Sulawesi, as well as on the neighboring islands of Selayar, Buton, Muna, Kabeana, Peleng, Lembeh and the Togian Islands (MacKinnon 1981, Wiles et al. 2002, Macdonald et al. 2005). By the early 1980s it was reported that this species was greatly reduced in population numbers in south-west Sulawesi, and in nearby Selayar Island, following the virtual deforestation of these areas changed into agriculture and human settlements (MacKinnon 1981, National Research Council 1983).
In 2002, an island wide survey found a pattern of a patchy species distribution throughout Sulawesi Island. There were no records of pigs in three areas in the north east peninsula, and low densities in the central region of the island. Populations in both these regions appear to have been affected by demand for pig meat in Minahasa and Palu areas, respectively (Riley 2002).
The species has also been introduced elsewhere in Indonesia, e.g. to the islands of Flores, Timor, Lendu and Simeulue. The wild pigs on some of these islands are strongly modified and there is now little doubt that S. celebensis has been domesticated, and transported to these areas as a domestic or feral form, probably during the early migrations of peoples. Animals thought to be on S. celebensis origin were reported from the islands of Roti and Sawu (Groves, 1983; Bell, 1987). Hybridized forms of S. celebensis with S. scrofa forms were reported to survive on a number of islands in this region, including Salawatti, Great Kei Island, Dobu, Seram, Ambon, Bacan, Ternate, Morotai and New Guinea (Groves 1981, 1983; Oliver and Brisbin 1993). Genetic information on wild pigs from Halmahera, previously referred to as feral S. celebensis, has shown that they have greater genetic affinity to the New Guinea pigs. mtDNA sequences showed that the New Guinea pigs had haplotypes that clustered with pigs from Halmahera, Hawaii and Vanuwatu and were found in the “Pacific clade” (Larson et al. 2005). This rules out a significant S. celebensis maternal input as previously proposed (Groves 1981). Feral S. celebensis have been reported from Flores, Timor, Lendu and Simeulue and Nias islands (Groves 1981), and this has been confirmed by mtDNA sequences for Flores (Dobney et al. 2008), but for the other islands this now needs to be reassessed.




