Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A., Fishpool, L.D.C., Boesman, P. and Kirwan, G.M. 2016. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 2: Passerines. Lynx Edicions and 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 |
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 |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent shelf island |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 2,870,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | decreasing | poor | suspected | 2016-2029 |
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 | 4.5 years | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The global population size has not been quantified, but the species is described as scarce to fairly common over much of its large Sundaic range (Wells 2007, Mann 2008, Eaton et al. 2016). It is therefore not considered likely to approach population size thresholds (<10,000 mature individuals) for listing as threatened.
Trend justification: Estimations on rates of population trend in this species are lacking. However, given its forest dependence, an ongoing rapid decline is suspected on the basis of extensive lowland forest loss throughout the Greater Sundas. Global Forest Watch (2022), using data from Hansen et al. (2013) and methods disclosed therein, indicates that forest loss of 24–28% has occurred over the past three generations, and these rates are not anticipated to cease or slow in the future. The species is therefore suspected to being undergoing a decline near-equal to that of forest loss: population declines of 20–29% are therefore suspected to have occurred over the past three generations, and are predicted to continue in the future.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Brunei | extant | native | yes | |||
Indonesia | extant | native | yes | |||
Malaysia | extant | native | yes | |||
Thailand | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Malaysia | Belum-Temenggor |
Malaysia | Bintang Range |
Malaysia | Central Titiwangsa Range |
Malaysia | Endau-Rompin |
Malaysia | Gunung Pueh |
Malaysia | Kelabit Highlands |
Malaysia | Kinabatangan floodplain |
Malaysia | Krau Wildlife Reserve |
Malaysia | Lambir Hills National Park |
Malaysia | Lanjak Entimau Wildlife Sanctuary |
Malaysia | Mount Kinabalu |
Malaysia | Mulu - Buda Protected Area |
Malaysia | Niah National Park |
Malaysia | Panti forest |
Malaysia | Selangor Heritage Park |
Malaysia | South-east Pahang peat swamp forest |
Malaysia | Taman Negara National Park |
Malaysia | Tanjung Datu-Samunsam Protected Area |
Thailand | Bala Sector, Hala-Bala Wildlife Sanctuary |
Thailand | Hala Sector, Hala-Bala Wildlife Sanctuary and Bang Lang National Park |
Thailand | Khao Luang |
Thailand | Khao Nor Chuchi |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Forest | Subtropical/Tropical Swamp | suitable | resident |
Altitude | 0 - 700 m | Occasional altitudinal limits | (max) 1060 m |
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 | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
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 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Rail-babbler Eupetes macrocerus. Downloaded from
https://datazone.birdlife.org/species/factsheet/rail-babbler-eupetes-macrocerus on 22/11/2024.
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 22/11/2024.