VU
Rhinoceros Hornbill Buceros rhinoceros



Taxonomy

Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - A3cd+4cd

Red List history
Year Category Criteria
2020 Vulnerable A3cd+4cd
2018 Vulnerable A3cd+4cd
2016 Near Threatened A2c+3c+4c
2012 Near Threatened A2c+3c+4c
2008 Near Threatened A2c; A3c; A4c
2004 Near Threatened
2000 Lower Risk/Near Threatened
1994 Lower Risk/Least Concern
1988 Lower Risk/Least Concern
Species attributes

Migratory status not a migrant Forest dependency high
Land-mass type continent
shelf island
Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 3,370,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size unknown - - -
Population trend decreasing poor inferred 2004-2044
Rate of change over the future 10 years/3 generations (longer of the two periods) 35-40% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 35-40% - - -
Generation length 14 years - - -

Population justification: The population size of this species has not been quantified. The species is widespread throughout its range, but occurs at low densities, even in suitable habitat (Poonswad et al. 2013).
In Peninsular Malaysia, Sungai Tekam Forestry Concession (Pahang State) population density was found to be 1.6 groups/km2 in primary forest and 2.3, 1.8, 1.2, 0.4 groups/km2 in 0-6 month, 1-2 year, 3-4, 5-6-year-old logged forest respectively (Johns 1987). In Kuala Lompat (Krau Wildlife Reserve) the population density was 2 individuals/km2 (Medway & Wells 1971). In Sarawak, Upper Baram and Batang Ai National Park had population densities of 0.27 individuals/km2 (Chin & Jantan 2001) and 0.96 individuals/km2 (Meredith 1995) respectively. In Sabah, Crocker Range Park and Tawau Hills Park had population densities of 0.94 individuals/km2 and 5.67 individuals/km2 respectively (Lakim & Biun 2005).

Trend justification: An analysis of deforestation between 2000 and 2012 estimated forest loss within the species's range at a rate equivalent to 35% over three generation lengths (42 years) (Tracewski et al. 2016). Being largely restricted to primary forests and intolerant of habitat conversion, the species is additionally threatened by hunting. Thus, its actual rate of population decline is likely greater than the estimate decline based on forest loss alone, possibly exceeding 35% over three generations. The rate of decline is therefore placed in the band 35-40% over three generations. Since this species has a long generation length, with three generations stretching over 42 years, there is insufficient evidence to calculate the magnitude of reduction over the past three generations. Assuming the recent rate of decline remains constant, the species is projected to decline by 35-40% over the next three generations.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Brunei extant native yes
Indonesia extant native yes
Malaysia extant native yes
Singapore extinct native yes
Thailand extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Malaysia Bako-Buntal Bay
Malaysia Belum-Temenggor
Malaysia Bintang Range
Malaysia Central Titiwangsa Range
Malaysia Danum Valley Conservation Area
Malaysia Danum-Linau
Malaysia Endau-Rompin
Malaysia Gunung Pueh
Malaysia Hose-Laga mountains
Malaysia Kabili-Sepilok
Malaysia Kelabit Highlands
Malaysia Kinabatangan floodplain
Malaysia Kledang Range
Malaysia Krau Wildlife Reserve
Malaysia Kulamba Wildlife Reserve
Malaysia Lambir Hills National Park
Malaysia Lanjak Entimau Wildlife Sanctuary
Malaysia Maliau Basin Conservation Area
Malaysia Mount Kinabalu
Malaysia Mulu - Buda Protected Area
Malaysia Nakawan Range
Malaysia Niah National Park
Malaysia Panti forest
Malaysia Pondok Tanjung Forest Reserve
Malaysia Sadong-Saribas coast
Malaysia Selangor Heritage Park
Malaysia Similajau National Park
Malaysia South-east Pahang peat swamp forest
Malaysia Tabin Wildlife Reserve
Malaysia Taman Negara National Park
Malaysia Tanjung Datu-Samunsam Protected Area
Malaysia Tawau Hills Park
Malaysia Ulu Muda
Malaysia Usun Apau plateau
Thailand Bu Do - Sungai Padi
Thailand Hala Sector, Hala-Bala Wildlife Sanctuary and Bang Lang National Park
Thailand Khao Banthad
Thailand Thaleban

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Lowland major resident
Forest Subtropical/Tropical Moist Montane marginal resident
Altitude 0 - 1750 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Annual & perennial non-timber crops - Agro-industry farming Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Annual & perennial non-timber crops - Small-holder farming Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Wood & pulp plantations - Agro-industry plantations Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Hunting & trapping terrestrial animals - Intentional use (species is the target) Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species mortality
Biological resource use Hunting & trapping terrestrial animals - Unintentional effects (species is not the target) Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Species mortality
Biological resource use Logging & wood harvesting - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion

Utilisation
Purpose Scale
Food - human subsistence, national
Handicrafts, jewellery, etc. subsistence, national
Pets/display animals, horticulture national, international

Recommended citation
BirdLife International (2024) Species factsheet: Rhinoceros Hornbill Buceros rhinoceros. Downloaded from https://datazone.birdlife.org/species/factsheet/rhinoceros-hornbill-buceros-rhinoceros on 22/12/2024.
Recommended citation for factsheets for more than one species: BirdLife International (2024) IUCN Red List for birds. Downloaded from https://datazone.birdlife.org/species/search on 22/12/2024.