|Scientific Name:||Bubalus depressicornis|
|Species Authority:||(C.H. Smith, 1827)|
|Taxonomic Notes:||There is still debate about whether Lowland Anoa (Bubalus depressicornis) and Mountain Anoa (Bubalus quarlesi) are distinct species (Burton et al. 2005). Two phenotypes of Anoa, characterized by body size, hair texture, horn shape, and body colours have been used by certain authors to justify the existence of two species. However, transitory morphs suggest that the real relationships are more complex, and poorly understood. For example several individuals photographed in zoos show a range of features considered diagnostic for the two species observed in single individuals as they grow to maturity (Mustari pers. comm). Sulawesi is a rather small territory, albeit geographically complex, so the speciation patterns of a large mammal pose a riddle to systematists. An enormous underlying variability (outward appearance, anatomy, chromosomes, proteins, DNA) has hitherto precluded a convincing classification, or has questioned the validity of an approach to group Anoa diversity into clear, reproducible types. Pattern-based classifications of zoo and museum specimens, most of which are devoid of reliable information as to their origin within Sulawesi, have always suffered from the later discovery of phenotypes with new combinations of supposedly diagnostic species characters.
Populations or individuals with combinations of features associated with one or other phenotype probably do not represent "hybrids" of two species, but various degrees of genetic introgression, or even primary clines of diverging evolutionary lineages, and they could perhaps differ in different regions of Sulawesi, depending on the degree of gene flow, and the characters affected. Given the ongoing uncertainty, every regional Anoa population should be considered worthy of conservation. The management units should at least be based on known origins from within Sulawesi, rather than on taxonomic schemes, which in the past have often proved incomplete. This has been the approach taken by the Indonesian Ministry of Forestry in publishing the National Strategy and Conservation Action Plan for Anoa 2013-2022 (2013).
The English common names of the two species relate to a still uncertain altitudinal separation (Groves 1969), with the large form (Lowland Anoa) purportedly inhabiting low-lying areas and the smaller form (Mountain Anoa) living at higher elevations (Burton et al. 2005).
|Red List Category & Criteria:||Endangered C1+2a(i) ver 3.1|
|Assessor(s):||Burton, J., Wheeler, P. & Mustari, A.|
|Contributor(s):||Mannullang, B., Schreiber, A. & Semiadi, G.|
This species is considered Endangered because its population is estimated to be less than 2,500 mature individuals, its rate of decline is believed to be greater than 20% over two generations (14 to 18 years), and no subpopulation is believed to number more than 250 mature individuals.
|Previously published Red List assessments:|
This species is endemic to Indonesia, where it is found only on Sulawesi and Buton Island off the southeast coast, with no records of either species of Anoas from other small neighbouring islands adjacent to Sulawesi (Burton et al. 2005). On Sulawesi it is found up to 1,000 m (G. Semiadi pers. comm. 2006). It remains uncertain whether the two putative species, Bubalus depressicornis and Bubalus quarlesi, are sympatric or parapatric in their distribution (Burton et al. 2005). Across Sulawesi, local distribution of Anoa species remains unclear, as they may occur in forest patches at different altitudes or sympatrically (Burton et al. 2005). Records of skulls and morphological descriptions of this species suggest it is present in the northern peninsula, as far east as the Bogani Nani-Wartabone National Park. It is also found across the central region and ranging to the tip of the eastern and southeastern peninsulas, but no longer present in the southwestern peninsula. The Lowland Anoa is also present in the central and north of Buton Island (Burton et al. 2005).
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||There are too few data to accurately quantify the species' current abundance; nevertheless, Anoa still appear to be distributed relatively widely within their known current range on Sulawesi. There have been declines of this species throughout Sulawesi, especially in the southern and northeastern peninsulas, with the decline attributed to hunting for meat and habitat loss (Indonesian Ministry of Forestry, 2013, Burton et al. 2005). The range is extremely fragmented, especially in the southern, northeastern and the south of the southeastern peninsulas of the island (Burton et al. 2005, B. Mannullang pers. comm. 2006). These declines probably began at the turn of the nineteenth century, with an increased rate of decline between 1980 and 2005 period (circa three generations), precipitously in some areas. The population size is unknown because there have been no island-wide or regional surveys which have attempted to estimate this, even for the largest populations. Estimating the population size is further complicated by the uncertain distribution of the two Anoa species. It is thought that there are fewer than 2,500 mature individuals. Most populations are becoming rapidly fragmented; suggesting that conservation of viable populations may soon require management of subpopulations (Burton et al. 2005). It is thought no subpopulation exceeds 250 mature individuals. Since the Lowland Anoa inhabits more accessible areas than the Mountain Anoa, the threats to this species, and thus the declines, are considered more serious for this species than for the Mountain Anoa.|
The Lowland Anoa populations in small reserves (e.g., Tanjung Amolengu Wildlife Reserve) and other forest fragments are threatened with local extinction. Even the populations in large protected areas and other large forest blocks are reported to be in decline as a result of heavy hunting pressure. O'Brien and Kinnaird (1996) report a 50 to 95% decline of this species in Tangkoko Nature Reserve in Northern Sulawesi in a 10-year period, with more recent surveys suggesting it is now locally extinct in in the reserve. The rate of population decline across their range is thought to be 20% over two generations (generation length of 7 to 9 years). The species’ ecology has been studied in the Tanjung Peropa and Tanjung Amolengo Wildlife Reserves in southeastern Sulawesi.
|Current Population Trend:||Decreasing|
|Habitat and Ecology:|
There is very little is known about the ecology and life history of the Anoas (Burton et al. 2005). Population densities were estimated in south east Sulawesi where estimates range from 1.1-1.6 animals/km² but with wide confidence limits (Mustari 2003, Burton et al. 2005) and Buton where density was estimated at 1.1 animals/km² (Wheeler 2004). Further estimates are as low as 0.07 animals/km² in north Sulawesi (O’Brien and Kinnaird 1996) and as high as 2.4 animals/km² from south east Sulawesi (Mustari 1995). On Buton island, Anoas appeared to use forests independent of their primary or secondary nature, the primary determinant of use being human activity in the forest (Dwiyahreni 2006, Wheeler et al. 2009). In Lore Lindu National Park, central Sulawesi track counts were highest in higher altitude areas away from the park’s fringes (Burton and MacDonald 2009, Okarda 2010). Riverine and lowland forests were preferred by Anoa compared to rocky-cliff forest in Tanjung Peropa Wildlife Reserve due to the availability of water sources, known food plants and fruit-bearing trees (Mustari 2003). In the past the species was reportedly common along coasts. Lowland Anoa are also found at high elevations in mountainous areas. Like other wild buffalo, Anoas wallow and bathe in pools of water and/or mud. It is probable that mineral springs or licks are also required, although Anoas are reported to drink seawater, which might fulfil their mineral needs in areas without licks or springs.
|Generation Length (years):||7-9|
|Use and Trade:||Hunting for food is considered to be a threat to this species. There is also a trade in live animals and in body parts (presumably for medicine), but this is not thought to constitute a threat.|
Land conversion to agriculture and hunting, mainly for food, are the two major threats to this species (Burton et al. 2005), as well as gold mining and other activities related to the collection of non-timber forest products (A. Priyono pers. comm. 2006). Recent reports indicate that hunting is by far the most serious threat. International trade in live animals or body parts is not thought to present a serious threat.
The species is listed on CITES Appendix I and fully protected under Indonesian law (Jahja 1987). Lowland Anoa occur in a number of protected areas (Indonesian Ministry of Forestry 2013, Burton et al. 2005). There are several key protected areas thought to hold significant populations of this species, including Lore Lindu National Park, Bogani Nani-Wartabone National Park, and Tanjung Peropa Nature Reserve on Sulawesi (Indonesian Ministry of Forestry 2013, Burton et al. 2005), as well as Lambusango Wildlife Reserve on Buton Island (Burton 2001). In 2013 the Indonesian Ministry of Forestry published a Strategy and Conservation Action Plan for Anoa 2013-2022. The vision of this plan is 'a stable population of Anoa in its wild habitat through reduced poaching (hunting) and illegal trade, maintenance of the existing habitat, through active involvement of the stakeholders'. A series of high priority sites for in situ conservation of Anoa have been identified: 11 in mainland Sulawesi, and two in Buton (Indonesian Ministry of Forestry 2013). These sites were selected based on a) representation of known subpopulations, extent of forest cover and connectivity between forested areas and status of management of area (whether sites were national parks, protected forests, restoration concessions). The plan also identifies protection from hunting, prevention of habitat loss, determining population status, education and training, and developing partnerships as important areas for future activities. It is too early to determine the impact of this new initiative. There is also on-going genetic and morphological research that aims to clarify the confusion that surrounds Anoa systematics.
A number of Lowland Anoa are in captivity, but the breeding program has been greatly hindered by the difficulties of assigning captive anoa to appropriate taxa. The captive population as of 257 animals. This consists of 46 in Europe (7th December 2015), 166 in North America and 45 in Asia (7th December 2015). In the American population, 13 individuals are in Association of Zoos and Aquariums institutions (9th December 2015) and 153 in non AZA North American institutions (pers. comm. March 2016). The sex of this latter group is not known. The sex ratio of known individuals is 43 males and 42 females. Within the Asia population of 45 individuals, 34 are kept in three Indonesian zoos (13 males and 21 females) (pers. comm. March 2016). Of these, a small number are thought to be Mountain Anoa, although the taxonomic status of most individuals remains unconfirmed (Nötzold 2013). The latest international studbook was published on 31 January 2013 (Nötzold 2013); this is currently being updated. There is a new initiative underway to implement a global species breeding programme to improve the genetic representation of the ex situ population.
|Citation:||Burton, J., Wheeler, P. & Mustari, A. 2016. Bubalus depressicornis. The IUCN Red List of Threatened Species 2016: e.T3126A46364222.Downloaded on 26 May 2017.|
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