|Scientific Name:||Elephas maximus ssp. sumatranus|
|Species Authority:||Temminck, 1847|
See Elephas maximus
While subspecies taxonomy of Elephas maximus has varied among authors, the most recent treatment (Shoshani and Eisenberg 1982) recognizes three subspecies: E. m. indicus on the Asian mainland, E. m. maximus on Sri Lanka, and E. m. sumatranus on the Indonesian island of Sumatra. Borneo's Elephants have traditionally been included in E. m. indicus (Shoshani and Eisenberg 1982) or E. m. sumatranus (Medway 1977, but see Fernando et al. 2003 and Cranbrook et al. 2008 for discussion of whether the elephants of Borneo are indigenous to the island). These subspecies designations were based primarily on body size and minor differences in coloration, plus the fact that E. m. sumatranus has relatively larger ears and an extra pair of ribs (Shoshani and Eisenberg 1982). The Sri Lankan subspecies designation is only weakly supported by analysis of allozyme loci (Nozawa and Shotake 1990), but not by analysis of mitochondrial DNA (mtDNA) sequences (Hartl et al. 1996, Fernando et al. 2000, Fleischer et al. 2001). However, current patterns of mtDNA variation suggest that the Sumatran subspecies is monophyletic (Fleischer et al. 2001), and consequently this taxon could be defined as an evolutionarily significant unit (ESU). This suggests that Sumatran Elephants should be managed separately from other Asian elephants in captivity, and is also an argument for according particularly high priority to the conservation of Sumatran Elephants in the wild.
|Red List Category & Criteria:||Critically Endangered A2c ver 3.1|
|Assessor(s):||Gopala, A., Hadian, O., Sunarto, ., Sitompul, A., Williams, A., Leimgruber, P., Chambliss, S.E. & Gunaryadi, D.|
|Reviewer(s):||Hedges, S., Desai, A. & Tyson, M.|
The Sumatran Elephant (E. m. sumatranus) meets criterion A2c for Critically Endangered (CR). Taking ca. 25 years as a single generation (sensu IUCN 2001) for Asian Elephants, then over 69% of potential Sumatran Elephant habitat has been lost within just one generation (the last 25 years) and the driving forces that are causing the habitat loss are still continuing essentially unchecked. There is clear direct evidence from two provinces (Riau and Lampung) to show that entire elephant populations have disappeared as a result of the habitat losses of the past 25 years: nine populations have been lost since the mid-1980s in Lampung (Hedges et al. 2005) and a 2009 survey of nine forest blocks in Riau that had elephant herds in 2007 revealed that six herds had gone extinct (Desai and Samsuardi 2009). That this pattern will continue seems certain.
Note that we use the term “potential elephant habitat” when discussing the rate of elephant habitat loss since 1985. This is because some of the forested areas that have been lost since 1985 elephants did not contain elephants in 1985; however, it is entirely reasonable to infer that elephants occurred much more widely across Sumatra in the 1930s than they did in 1985 since the 1985 elephant distribution map was the first time we had an island-wide understanding of elephant distribution on the island, and it was not a complete picture even then. Thus we infer that all the forest lost since 1985 was elephant habitat in the 1930s, or – in other words – the forest lost since 1985 alone represents a loss of 69% of Sumatran Elephant habitat since the 1930s (three elephant generations). Since elephants almost certainly occurred in areas outside their 1985 distribution in the 1930s and because much of the forest and other land cover types lost have been the better quality (preferred) lowland elephant habitat, we conclude that the inferred or suspected population size reduction for Sumatran Elephants over the last three generations must have been at least 80%. This conclusion is greatly strengthened by the fact that much of the remaining forest cover is in blocks smaller than 250 km², which are too small to contain viable elephant populations: this has the effect of increasing the real impact – on elephant numbers – of habitat loss beyond the figures suggested by forest loss alone. Therefore E. m. sumatranus meets criterion A2c for Critically Endangered (CR).
|Range Description:||Home to the Sumatran Elephant subspecies (E. m. sumatranus), Sumatra is thought to hold some of the most significant Asian Elephant populations outside of India. Yet, within the Asian Elephant’s range, Sumatra has experienced one of the most rapid deforestation rates (Uryu et al. 2010).|
|Range Map:||Click here to open the map viewer and explore range.|
In mid 1980s, when about 50% of natural forest remained on the island, elephant populations persisted in 44 discrete populations on all of the island’s eight provinces (Hedges et al. 2005).
1985: An island-wide rapid survey suggested that between 2,800 and 4,800 elephants lived in the wild in 44 ranges in all eight mainland provinces of Sumatra (Blouch and Haryanto 1984). Riau Province was believed to have the largest elephant population in Sumatra.
2002: Sumatra was still thought to contain some of the largest populations of Asian elephants outside of India and Sri Lanka. Rigorous dung density based surveys in Lampung Province’s two national parks, Bukit Barisan Selatan and Way Kambas, produced population estimates of 498 (95% CI=[373, 666]) and 180 (95% CI=[144, 225]) elephants, respectively. But province-wide surveys at the same time also showed that by 2002 elephants had gone locally extinct in nine of 12 elephant ranges recorded in Lampung in the early 1980s (Hedges et. al. 2005).
2007: Guesstimates suggested that between 2,400 and 2,800 elephants live in the wild (Soehartono et al. 2007). Given the very high number of elephants brought into captivity since 1985 (Mikota et al. 2003), the high mortality experienced during these government capture-and-translocation operations, and the high numbers of elephants lost to retaliatory killing after human–elephant conflict (WWF 2008) and poaching (based on local newspaper reports), it is highly likely that Sumatra’s total elephant population size in 1985 might actually have been greater than even that year’s high estimate of 4,800 elephants suggests. In any case, in only one generation (between 1985 and 2007) Sumatra may have lost up to 50% of its elephants.
2008: By 2008, elephants had become locally extinct in 23 of the 43 ranges identified in Sumatra in 1985, indicating a very significant decline of the Sumatran elephant population up to that time. By 2008, the elephant was locally extinct in one of Sumatra’s eight mainland provinces (West Sumatra) and at risk of being lost from North Sumatra Province too. Only ca. 350 elephants survived across nine separate ranges in Riau Province, which in 1985 was considered to have the largest elephant population in Sumatra with over 1,600 individuals.Post-2008: Simple extrapolations from past population history suggests that Riau’s last surviving elephants may soon disappear if the current trend of forest loss continues (Uryu et al. 2008). Indeed, a 2009 survey of nine forest blocks in Riau that had elephant herds in 2007 revealed that six herds had gone extinct (Desai and Samsuardi 2009).
Systematic study on the population of Sumatran Elephants is lacking from most of the elephant’s distributional range. Province-wide assessments have been conducted in Riau (Desai and Samsuardi 2009) and Lampung (Hedges et al. 2005). However, rigorous population estimates are only available from two protected areas in Lampung, namely Way Kambas National Park and Bukit Barisan Selatan National Park (Hedges et al. 2005, Soehartono et al. 2007).
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||
Elephants largely use lowland forests and gentle hills below an altitude of 300 m. While the elephants in Sumatra may have habitat use patterns that differ, it is generally known from long-term studies of elephants across Asia that lowland forests are a preferred habitat (Alfred el. al. 2005, Williams 2010). Forest loss in the lowlands is higher than forest loss at all altitudes and including habitats such as peat forests, where elephants are not present.
See the Supplementary Material for further information about national loss of natural forest in Sumatra.
|Use and Trade:||The Asian elephant is hunted for ivory, food, leather and other products. Live animals are also removed from the wild and used in forestry operations and for ceremonial purposes.|
|Major Threat(s):||Due to conversions of forests into human settlement and agricultural areas, many of the Sumatran Elephant populations have come into serious conflicts with human. As the results, many wild elephants have been removed from the wild, or directly killed. In addition to killing related to conflicts, elephants are also targets of illegal killing for their ivory. Now, Sumatran Elephant lives only in seven provinces, many of which are under increased pressure of habitat loss and imminent conflicts with human.|
|Conservation Actions:||Although as a species Sumatran Elephants are protected under Indonesia law, 85% of their habitats which are located outside of protected areas, are outside of the protection system and likely to be converted to agricultural and other purposes.|
Alfred, R., Williams, A.C., Vertefeuille, J., Payne, J., Andau, P., Ambu, L., Sipangkui, S. and Lim, A. 2006. Satellite Tracking of Borneo's Pygmy Elephants. WWF Malayasia, Kuala Lumpur.
Blouch, R. A. and Haryanto. 1984. Elephants in southern Sumatra. Unpublished report, IUCN/WWF Project 3033, Bogor, Indonesia.
Cranbrook, Earl of, Payne, J. and Leh, C. M. U. 2008. Origin of the elephants Elephas maximus L. of Borneo. Sarawak Museum Journal.
Desai, A. and Samsuardi. 2009. Status of elephant habitat and population in Riau. In: WWF (ed.). Pekanbaru, Indonesia.
Fernando, P., Pfrender, M. E., Encalada, S. E. and Lande, R. 2000. Mitochondrial DNA variation, phylogeography and population structure of the Asian elephant. Heredity 84: 362–372.
Fernando, P., Vidya, T. N. C., Payne, J., Stuewe, M., Davison, G., Alfred, R. J., Andau, P., Bosi, E., Kilbourn, A. and Melnick, D. J. 2003. DNA analysis indicates that Asian elephants are native to Borneo and Are therefore a high priority for conservation. PLoS Biology 1(1): 110-115.
Fleischer, R. C., Perry, E. A., Muralidharan, K., Stevens, E. E. and Wemmer, C. M. 2001. Phylogeography of the Asian elephant (Elephas maximus) based on mitochondrial DNA. Evolution 55: 1882–1892.
Gaveau, D.L.A., Wandonoc, H. and Setiabudid, F. 2007. Three decades of deforestation in southwest Sumatra: Have protected areas halted forest loss and logging, and promoted re-growth? Biological Conservation 134(4): 495–504.
Hartl, G. B., Kurt, F., Tiedemann, R., Gmeiner, C., Nadlinger, K., Mar, K. U. and Rübel, A. 1996. Population genetics and systematics of Asian elephant (Elephas maximus): a study based on sequence variation at the cyt b gene of PCR-amplified mitochondrial DNA from hair bulbs. Zeitschrift für Säugetierkunde 6: 285-294.
Hedges, S., Tyson, M. J., Sitompul, A. F., Kinnaird, M. F., Gunaryadi, D. and Aslan. 2005. Distribution, status, and conservation needs of Asian elephants (Elephas maximus) in Lampung Province, Sumatra, Indonesia. Biological Conservation 124: 35–48.
IUCN. 2001. IUCN Red List Categories and Criteria: version 3.1. IUCN Species Survival Commission. IUCN, Gland, Switzerland and Cambridge, UK.
IUCN. 2011. IUCN Red List of Threatened Species (ver. 2011.2). Available at: http://www.iucnredlist.org. (Accessed: 10 November 2011).
Kinnaird, M.F., Sanderson, E.W., O'Brien, S.J., Wibisono, H.T. and Woolmer G. 2003. Deforestation trends in a tropical landscape and implications for endangered large mammals. Conservation Biology 17(1): 245–257.
Medway, L. 1977. Mammals of Borneo. Monograph of the Malaysian Branch of the Royal Asiatic Society 7: 1-172.
Mikota, S.K., Hammatt, H. and Finnegan, M. 2003. Occurrence and prevention of capture wounds in Sumatran elephants (Elephas maximus sumatranus). Proceedings of the Joint Conference of the American Association of Zoo Veterinarians 2003: 291-293.
Nozawa, K. and Shotake, T. 1990. Genetic differentiation among local populations of Asian elephant. Zeitschrift fur Zoologische Systematik und Evolutionsforschung 28: 40–47.
Shoshani, J. and Eisenberg, J. F. 1982. Elephas maximus. Mammalian Species 182: 1–8.
Soehartono, T., Susilo, H.D., Sitompul, A.F., Gunaryadi, D., Purastuti, E.M., Azmi, W., Fadhli, N. and Stremme, C. 2007. Strategi dan rencana aksi konservasi gajah Sumatera dan gajah Kalimantan 2007-2017. Jakarta.
Uryu, Y., Mott, C., Foead, N., Yulianto, K., Budiman, A., Setiabudi, Takakai, F., Nursamsu, Sunarto, Purastuti, E., Fadhli, N., Hutajulu, C.M.B., Jaenicke, J., Hatano, R., Siegert, F. and Stüwe, M. 2007. Deforestation, forest degradation, biodiversity loss and CO2 emissions in Riau, Sumatra, Indonesia. WWF Indonesia, Jakarta.
Uryu, Y., Purastuti, E., Laumonier, Y., Sunarto, Setiabudi, Budiman, A., Yulianto, K., Sudibyo, A., Hadian, O., Kosasih, D.A. and Stüwe, M. 2010. Sumatra’s Forests, Their Wildlife and the Climate. Windows in Time: 1985, 1990, 2000 and 2009. A quantitative assessment of some of Sumatra’s natural resources submitted as technical report by invitation to the National Forestry Council (DKN) of Indonesia. WWF Indonesia, Jakarta.
Van Steenis, C.G. 1935. Maleische vegetatieschetsen. Tijdschrift v.d. Nederlandsche Aardijkskundig Genootscha 52: 25-67, 171-203, 363-398.
Williams, A.C. 2010. The ecology and population parameters of Asian elephants in NW India. Lambert Academic Publishing, Saarbrücken.
WWF. 2008. Common Ground: Solutions for Reducing the Human, Economic andConservation Costs of Human-Wildlife Conflict. WWF Report. Gland, Switzerland.
|Citation:||Gopala, A., Hadian, O., Sunarto, ., Sitompul, A., Williams, A., Leimgruber, P., Chambliss, S.E. & Gunaryadi, D. 2011. Elephas maximus ssp. sumatranus. The IUCN Red List of Threatened Species 2011: e.T199856A9129626. . Downloaded on 30 April 2016.|