Bubalus mindorensis 

Scope: Global
Status_ne_offStatus_dd_offStatus_lc_offStatus_nt_offStatus_vu_offStatus_en_offStatus_cr_onStatus_ew_offStatus_ex_off

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Mammalia Cetartiodactyla Bovidae

Scientific Name: Bubalus mindorensis
Species Authority: Heude, 1888
Common Name(s):
English Tamaraw, Mindoro Dwarf Buffalo
French Tamarau
Spanish Búfalo de Mindoro

Assessment Information [top]

Red List Category & Criteria: Critically Endangered C1+2a(ii) ver 3.1
Year Published: 2016
Date Assessed: 2016-04-27
Assessor(s): Boyles, R., Schutz, E. & de Leon, J.
Reviewer(s): Burton, J.
Contributor(s): Custodio, C., Duckworth, J.W., Gonzales, J.C., Hedges, S. & Huffman, B.
Justification:
The species qualifies for inclusion in Critically Endangered under criteria C1+2a(ii). The number of mature individuals in the population is estimated to be less than 250, with a continuing decline estimated at over 25% over the next three generations (generation length estimated at 10 years). In addition, over 95% of individuals are presumed to be in one subpopulation (Mount Iglit-Baco National Park), which is less than 5,000 hectares in area.
Previously published Red List assessments:

Geographic Range [top]

Range Description:The Tamaraw is endemic to the Philippine island of Mindoro (9,735 km² in area), where it was formerly widespread across the island (S. Hedges and W. Duckworth pers. comms. 2000, Heaney et al. 2002). However, the current range is estimated to cover less than 10,000 hectares (Schütz 2015) and limited to the mountainous interior of the Island: Mount Iglit-Baco National Park (the largest protected area of Mindoro located in the centre of the Island), the Aruyan-Malati Tamaraw Reservation (Municipality of Sablayan), and Mount Calavite Wildlife Sanctuary in the north of the Island represent the three known surviving subpopulations and are all located on the Occidental part of Mindoro (Custodio et al. 1996, de Leon et al. 1996). Few other isolated groups are suspected to exist outside these subpopulations (Schütz 2015). The species was more widespread prehistorically in the Philippines, with Pleistocene epoch records from Luzon (Beyer 1957 in Kuehn 1986).
Countries occurrence:
Native:
Philippines
Additional data:
Estimated area of occupancy (AOO) - km2:100
Number of Locations:3
Lower elevation limit (metres):200
Upper elevation limit (metres):1800
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:In 2016, three separate subpopulations are known to survive on Mindoro. Population estimates undertaken have increased in frequency and have benefited from improved techniques and equipment over time. Based on most recent surveys and animal counts the minimum total population is estimated at around 430 individuals with 50 to 70% of these mature individuals (Boyles 2016). The subpopulation of Mount Iglit-Baco National Park, as of April 2016 was estimated to number approximately 413 individuals according to the last Tamaraw population count operation. The estimated number of individuals has increased subsequently since the start of the counting operation in 2000, but it is highly probable that the observed increase is both a reflection of improved estimates as well as immigration from animals coming from outside the counting area, rather than population growth (Schütz 2015). Nowadays this subpopulation is confined to the so called "core zone of the monitoring" at the south-west edge of the protected area, where the annual counting takes place and where regular ranger patrols ensure relative protection against poaching and disturbance. Even so, the area of occupancy of the species within the zone has been drastically decreasing since two decades from 5,000 hectares to only 2,000 hectares (Schütz 2015).

The subpopulation on Mount Calavite (the most northerly site) in 2004 had an estimated 15 individuals based on faecal matter and animal tracks; there has been only one confirmed sighting. The current population is assumed to be much lower with no sightings in several years (pers. comm. 2014). The subpopulation of Aruyan-Malati had an estimated population of 15 to 20 individuals in the 2000s (TCP results of the 2007 field survey has assessed around 16 animals). According to recent surveys and interviews of local communities, a maximum of 12 animals might still survive within a restricted area of less than 1,000 hectares (Schütz 2015). Also local communities living in remote areas of the centre of the island report the presence of the species in at least three other sites, in Mount Halcon range, the upper Amnay river (Eagle Pass area) and the east side of Mount Wood, but this information must be confirmed.

An estimated continuing decline of 25% over the next three generations (approximately 30 years) does not seem unreasonable given that the number of subpopulations reportedly declined from five or six to three between 1990 and now, with the population of Mt Calavite and Aruyan-Malati which can be considered in a critical situation.
Current Population Trend:Decreasing
Additional data:
Number of mature individuals:220-300Continuing decline of mature individuals:Yes
Population severely fragmented:No
No. of subpopulations:3

Habitat and Ecology [top]

Habitat and Ecology:Formerly, Tamaraw were found across the whole of Mindoro from sea level to the high peaks (to over 1,800 m), inhabiting open grassland or forest glades, thick bamboo-jungle, marshy river valleys, and low to mid-elevation forests (Rabor 1977). Currently the species is confined to a few remote areas over 200 m, and is most often recorded in secondary forest and mixed forest/grassland (Kuehn 1986, Custodio et al. 1996, Heaney et al. 2002).

Tamaraw are largely solitary, although females occur with offspring (Talbot and Talbot 1966). Males and females occasionally associate temporarily throughout the year (Custodio et al. 1996), which is similar to other bovine species, such as African Buffalo, Banteng and Gaur. The solitary nature of the species is probably an adaptation to forest habitats, where large groups would prove to be a hindrance (Eisenberg 1966, in Kuehn 1986).

Tamaraw feed primarily on grasses, as well as young bamboo shoots, in open grasslands, resting within tall grasses or dense forest (Talbot and Talbot 1966). Although formerly diurnal, Tamaraw have become largely nocturnal due to human encroachment and disturbance (Talbot and Talbot 1966). Within its "core zone" inside Mount Iglit-Baco National Park, the Tamaraw again
shows a rather diurnal behaviour and can be seen in larger groups, which can be explained by the relative protection they benefit from there.
Systems:Terrestrial
Generation Length (years):10

Use and Trade [top]

Use and Trade:

Tamaraw are used for local consumption and in the past for sport hunting.

Threats [top]

Major Threat(s): In the 20th century, the main threat to the Tamaraw was habitat loss due to farming by resettled and local people, with high human population growth rates in and around its remaining habitat. In some areas, fires set for agriculture are a threat to the species' habitat. Cattle ranching and farming activities pose a number of threats, including the risk of diseases spreading to the Tamaraw from livestock and burning of pastures leading to a reduced number of palatable grass species. Historically, Tamaraw were hunted for both subsistence and sport, which led to a period of drastic decline in numbers of individuals and populations (Rabor 1977). Hunting was carefully regulated prior to World War II, but since then a growing human population, logging operations, ranching, and widespread availability of firearms on Mindoro have caused a dramatic decline in numbers (Talbot and Talbot 1966). Since the 1980s, sport hunting has reduced due to a decline in the Tamaraw population, closure of nearby ranches, and more intensive patrolling and awareness activities since the establishment of the protected area. International trade in this species or its derivatives has not been reported. Although protected by law, the illegal capture and killing of this species continues.

Nowadays the main threat to the species stands in the lack of options for the remaining tamaraw populations to disperse and increase their range due to human pressure and shortage of undisturbed natural corridors (Schütz 2015). Poaching and illegal activities from lowlander Mindorenos pose a serious problem for wildlife. Besides this, traditional hunting activities from local indigenous communities in Tamaraw areas are a serious source of disturbance and possible cause of injury to tamaraw even if the species is not targeted (pit fall trap, snare trap). Moreover, land-use pressure from local indigenous communities is generally increasing in Mindoro due to population growth and incapability of those people to expand in lowland areas that are now occupied by new settlers.

Conservation Actions [top]

Conservation Actions: The Tamaraw is listed on CITES (the Convention on International Trade in Endangered Species of Wild Fauna and Flora) Appendix I. Tamaraw receive total protection under Philippine law. The largest of the three known subpopulations occurs in Mount Iglit-Baco National Park. A small number of Tamaraw are held in captivity in the Philippines, but the captive breeding program has had no success. Of the 21 individuals captured around 1982, there were nine individuals remaining in 1997. As of 2015 only one animal, born in captivity, was still alive and held in a half hectare enclosure. To date there are no further plans for captive breeding and the subject remains controversial. The original captive breeding programme consisted of placing the animals in a semi-natural "gene pool" on Mindoro, but these animals were not intensively managed, nor were the husbandry techniques focused on building a large captive population.

Few initiatives have been undertaken recently to address the critical situation of the species: the proclamation of the Aruyan-Malati area as “Critical Habitat” is underway and shall lead to better protection under a legal framework. Moreover, a general Protected Area Management Plan for Mount Iglit-Baco National Park shall be implemented in the near future and lead to the creation of a proper zoning system and consistent habitat management approach with the residing indigenous communities. A strictly protected zone has been already outlined within the core zone of the monitoring with no hunting activity measures.

Required research for this species includes to continue the island wide population survey to update the actual range of the species and determine if there are any additional extant populations. There is also a need for improved habitat conservation through effective management, which passes through better integration of the indigenous mangyan communities living within the range of the Tamaraw into habitat management plans. This must start by furthering ethno-ecological studies to better understand these communities, their claim, subsistence needs, their pattern of land-use (including the slash and burn agriculture) and vision upon the environment. Priority shall be first given to the remaining existing populations by securing and expending their range. In addition, the feasibility and need for a new captive breeding programme should be assessed.

Classifications [top]

1. Forest -> 1.6. Forest - Subtropical/Tropical Moist Lowland
suitability:Suitable  major importance:Yes
1. Forest -> 1.9. Forest - Subtropical/Tropical Moist Montane
suitability:Suitable  major importance:Yes
3. Shrubland -> 3.6. Shrubland - Subtropical/Tropical Moist
suitability:Suitable  major importance:Yes
4. Grassland -> 4.6. Grassland - Subtropical/Tropical Seasonally Wet/Flooded
suitability:Suitable  major importance:Yes
4. Grassland -> 4.7. Grassland - Subtropical/Tropical High Altitude
suitability:Suitable  major importance:Yes
1. Land/water protection -> 1.1. Site/area protection
1. Land/water protection -> 1.2. Resource & habitat protection
2. Land/water management -> 2.1. Site/area management
3. Species management -> 3.1. Species management -> 3.1.1. Harvest management
3. Species management -> 3.4. Ex-situ conservation -> 3.4.1. Captive breeding/artificial propagation
4. Education & awareness -> 4.1. Formal education
4. Education & awareness -> 4.2. Training
4. Education & awareness -> 4.3. Awareness & communications
5. Law & policy -> 5.1. Legislation -> 5.1.1. International level
5. Law & policy -> 5.1. Legislation -> 5.1.2. National level
5. Law & policy -> 5.4. Compliance and enforcement -> 5.4.1. International level
5. Law & policy -> 5.4. Compliance and enforcement -> 5.4.2. National level
5. Law & policy -> 5.4. Compliance and enforcement -> 5.4.3. Sub-national level

In-Place Research, Monitoring and Planning
In-Place Land/Water Protection and Management
  Occur in at least one PA:Yes
In-Place Species Management
  Subject to ex-situ conservation:No
In-Place Education
  Subject to recent education and awareness programmes:Yes
  Included in international legislation:Yes
  Subject to any international management/trade controls:Yes
1. Residential & commercial development -> 1.1. Housing & urban areas
♦ timing:Ongoing    
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

2. Agriculture & aquaculture -> 2.1. Annual & perennial non-timber crops -> 2.1.2. Small-holder farming
♦ timing:Ongoing    
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

2. Agriculture & aquaculture -> 2.3. Livestock farming & ranching -> 2.3.2. Small-holder grazing, ranching or farming
♦ timing:Ongoing    
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

5. Biological resource use -> 5.1. Hunting & trapping terrestrial animals -> 5.1.1. Intentional use (species is the target)
♦ timing:Ongoing    
→ Stresses
  • 2. Species Stresses -> 2.1. Species mortality

7. Natural system modifications -> 7.1. Fire & fire suppression -> 7.1.1. Increase in fire frequency/intensity
♦ timing:Ongoing    
→ Stresses
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

8. Invasive and other problematic species, genes & diseases -> 8.1. Invasive non-native/alien species/diseases -> 8.1.1. Unspecified species
♦ timing:Ongoing    
→ Stresses
  • 2. Species Stresses -> 2.1. Species mortality

8. Invasive and other problematic species, genes & diseases -> 8.2. Problematic native species/diseases -> 8.2.1. Unspecified species
♦ timing:Ongoing    
→ Stresses
  • 2. Species Stresses -> 2.1. Species mortality

1. Research -> 1.2. Population size, distribution & trends
1. Research -> 1.3. Life history & ecology
1. Research -> 1.5. Threats
1. Research -> 1.6. Actions
3. Monitoring -> 3.1. Population trends

Bibliography [top]

Alcasid, G. L. 1977. Vanishing Philippine Wildlife. Lahing Pilipino Publishing Inc, Philippines.

Baillie, J. and Groombridge, B. (comps and eds). 1996. 1996 IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

Boyles, R. 2015. Tamaraw Month Celebration /Biodiversity Management Bureau activity report. Unpublished. . Department of Environment and Natural Resources.

Boyles, R. 2016. Annual Tamaraw Population Count Results 2016. Unpublished report. . Tamaraw Conservation Program. Department of Environment and Natural Resources.

Corbet, G.B. 1978. The Mammals of the Palaearctic Region: a Taxonomic Review. British Museum (Natural History) and Cornell University Press, London, UK and Ithaca, NY, USA.

Cox, R. and Woodford, M. 1990. A Technical Evaluation of the Philippine Tamaraw Conservation Programme.

Custodio, C.C., Lepiten, M.V. and Heaney, L.R. 1996. Bubalus mindorensis. Mammalian Species 520: 1-5.

de Leon, J., Lawas, N., Escalada, R., Ong, P., Callo, R., Hedges, S., Ballou, J., Armstrong, D. and Seal, U. S. 1996. Tamaraw (Bubalus mindorensis) Population and Habitat Viability Assessment Report.

Groombridge, B. (ed.). 1994. IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

Heaney, L.R., Balete, D.S., Dollar, M.L., Alcala, A.C., Dans, A.T.L., Gonzales, P.C., Ingle, N.R., Lepiten, M.V., Oliver, W.L.R., Ong, P.S., Rickart, E.A., Tabaranza Jr., B.R. and Utzurrum, R.C.B. 1998. A synopsis of the mammalian fauna of the Philippine Islands. Fieldiana: Zoology (New Series) 88: 1–61.

Heaney, L.R., Walker, E.K., Tabaranza, B.R., Jr. and Ingle, N. 2002. Mammalian diversity in the Philippines: an assessment of the adequacy of current data. Sylvatrop, The Philippine Forest Research Journal 10: 6–27.

Hedges, S. In press. Asian Wild Cattle and Buffaloes: Status Report and Conservation Action Plan. IUCN/SSC Asian Wild Cattle Specialist Group, Gland, Switzerland.

Hilton-Taylor, C. (ed.). 2000. 2000 IUCN Red List of Threatened Species. IUCN, Gland, Switzerland and Cambridge, UK.

IUCN. 1990. IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

IUCN. 2016. The IUCN Red List of Threatened Species. Version 2016-2. Available at: www.iucnredlist.org. (Accessed: 04 September 2016).

IUCN Conservation Monitoring Centre. 1986. 1986 IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

IUCN Conservation Monitoring Centre. 1988. IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

Kuehn, D. W. 1986. Population and social characteristics of the Tamarao (Bubalus mindorensis). Biotropica 18: 263-266.

Lustria, U. M. and Callo, R. A. 1992. Tamaraw (Bubalus mindorensis Heude) census in Mt. Iglit, Occidental Mindoro and gene pool farm. Sylvatrop, The Philippine Forest Research Journa 1: 81-90.

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Schütz, E. 2015. Records of Mindoro Warty Pig (Sus oliveri) in the interior of Mindoro Island – Philippines. Suiform Soundings – newsletter of the IUCN/SSC Wild Pig, Peccary, and Hippo Specialist Groups 13(2): 13-15.

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Citation: Boyles, R., Schutz, E. & de Leon, J. 2016. Bubalus mindorensis. In: The IUCN Red List of Threatened Species 2016: e.T3127A50737640. . Downloaded on 25 September 2016.
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