Data Zone
Taxonomic note
Caloramphus fuliginosus and C. hayii (del Hoyo and Collar 2014) were previously lumped as Calorhamphus fuliginosus following Sibley and Monroe (1990, 1993).
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.
| Critically Endangered | Endangered | Vulnerable |
|---|---|---|
| - | - | - |
| Year | Category | Criteria |
|---|---|---|
| 2022 | Near Threatened | A2c+3c+4c |
| 2016 | Near Threatened | A2c+3c+4c |
| 2014 | Near Threatened | A2c+3c+4c |
| 2012 | Not Recognised | |
| 2008 | Not Recognised | |
| 2004 | Not Recognised | |
| 2000 | Not Recognised | |
| 1994 | Not Recognised | |
| 1988 | Not Recognised |
| Migratory status | not a migrant | Forest dependency | high |
| Land-mass type | Average mass | 43 g |
| Estimate | Data quality | |
|---|---|---|
| Extent of Occurrence (breeding/resident) | 1,170,000 km2 | |
| Severely fragmented? | no | - |
| Estimate | Data quality | Derivation | Year of estimate | |
|---|---|---|---|---|
| Population size | unknown | - | - | - |
| Population trend | decreasing | - | suspected | 2016-2027 |
| Rate of change over the past 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
| Rate of change over the future 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
| Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
| Generation length | 3.7 years | - | - | - |
| Number of subpopulations | 2-100 | - | - | - |
| Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The global population size has not been quantified, but the species is reported to be fairly common to common in most of its range (Wells 1999, del Hoyo et al. 2002).
Trend justification: Remote sensing data (Global Forest Watch 2021, using Hansen et al. [2013] data and methods disclosed therein) indicate that forest cover loss in this species range has been 25-30% over the past three generations (11.1 years; Bird et al. 2020). Although this species is suspected to occur at higher densities in primary and selectively logged forest than plantations, it does occur in the latter (Wells 1999) such that the rate of decline is suspected to be no higher than that of forest loss, and so is suspected to be 20-29% over three generations. The declines are suspected to continue at a similar rate into the future.
| Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
|---|---|---|---|---|---|---|
| Indonesia | extant | native | yes | |||
| Malaysia | extant | native | yes | |||
| Myanmar | extant | native | yes | |||
| Singapore | extinct | native | yes | |||
| Thailand | extant | native | yes |
| Country/Territory | IBA Name |
|---|---|
| Malaysia | Belum-Temenggor |
| Malaysia | Bintang Range |
| Malaysia | Endau-Rompin |
| Malaysia | Kledang Range |
| Malaysia | Krau Wildlife Reserve |
| Malaysia | Nakawan Range |
| Malaysia | Panti forest |
| Malaysia | Pondok Tanjung Forest Reserve |
| Malaysia | Selangor Heritage Park |
| Malaysia | South-east Pahang peat swamp forest |
| Malaysia | Taman Negara National Park |
| Malaysia | Tanjung Tuan |
| Malaysia | Ulu Muda |
| Thailand | Bala Sector, Hala-Bala Wildlife Sanctuary |
| Thailand | Bu Do - Sungai Padi |
| Thailand | Hala Sector, Hala-Bala Wildlife Sanctuary and Bang Lang National Park |
| Thailand | Khao Luang |
| Thailand | Khao Nor Chuchi |
| Thailand | Thaleban |
| Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
|---|---|---|---|
| Artificial/Terrestrial | Plantations | suitable | resident |
| Artificial/Terrestrial | Subtropical/Tropical Heavily Degraded Former Forest | suitable | resident |
| Forest | Subtropical/Tropical Moist Lowland | major | resident |
| Forest | Subtropical/Tropical Swamp | suitable | resident |
| Altitude | 0 - 750 m | Occasional altitudinal limits | (max) 1060 m |
| Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
|---|---|---|---|---|---|---|---|---|---|
| Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
| Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
| Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
| Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
| Purpose | Scale |
|---|---|
| Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Malay Brown Barbet Caloramphus hayii. Downloaded from
https://datazone.birdlife.org/species/factsheet/malay-brown-barbet-caloramphus-hayii 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.