Taxonomic note
Alophoixus bres, A. frater and A. tephrogenys (del Hoyo and Collar 2016) were previously lumped as A. bres following Sibley and Monroe (1990, 1993).
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 |
---|---|---|
- | - | A2cd+3cd+4cd |
Year | Category | Criteria |
---|---|---|
2020 | Vulnerable | A2cd+3cd+4cd |
2016 | Least Concern | |
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 | medium |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 3,310,000 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | decreasing | - | inferred | 2014-2024 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Generation length | 2.8 years | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The species is described as common to very common, and locally numerous across Thailand and Malaysia (del Hoyo et al. 2020, J. Eaton in litt. 2020). Population densities are estimated to be 10-14.5 individuals/km2 (observed across logged forests of Borneo and Sumatra; del Hoyo et al. 2020). Based on recent concerns of the rate of trapping pressures inflicted across the species's range however, it is likely that the population has lowered considerably. Thus, due to high uncertainty, the population size has not been quantified.
Trend justification: Based on a recent analyses by Symes et al. (2018), the species was considered to be undergoing a decline of 73.8% over a 10-year period, as estimated using data gathered between 2000-2015. Declines were attributed to the combined effect of habitat loss and trapping pressures (Symes et al. 2018, [also Tracewski et al. 2016]). However, due to the species's tolerance to some extent of forest degradation, the rate of decline is thought to not be as significant. Additionally, Harris et al. (2016) show that the species may have undergone a slight increase (c. 0.148 as estimated by a mean coefficient) during 1998-2011, observed during field sampling at Way Canguk Research and Training Area, in the Bukit Barisan Selatan National Park.
Furthermore, in comparison to the Brown-cheeked Bulbul Alophoixus bres, undergoing a very rapid decline of at least 50% across 10 years (S. Marsden in litt. 2020) based on more significant rates of exploitation and its subsequent disappearance from many sites across its range, it is suspected that A. tephrogenys, although subjected to population reduction, is not equivalent to the rate at which A. bres has declined. Thus, the species is thought to be experiencing a rapid decline of 30-49% over a three-generation period. A continued population decline can be inferred using numbers recorded in bird markets; 34 birds observed in July 2015 as compared to only 5 birds observed in July 2019 (J. Eaton in litt. 2020).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Brunei | extant | native | yes | |||
Indonesia | extant | native | yes | |||
Malaysia | extant | native | yes | |||
Myanmar | extant | native | yes | |||
Thailand | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Malaysia | Belum-Temenggor |
Malaysia | Bintang Range |
Malaysia | Danum Valley Conservation Area |
Malaysia | Endau-Rompin |
Malaysia | Gunung Pueh |
Malaysia | Kabili-Sepilok |
Malaysia | Kinabatangan floodplain |
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 | Selangor Heritage Park |
Malaysia | Similajau National Park |
Malaysia | Tabin Wildlife Reserve |
Malaysia | Taman Negara National Park |
Malaysia | Tanjung Datu-Samunsam Protected Area |
Malaysia | Tawau Hills Park |
Malaysia | Ulu Muda |
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 Moist Montane | suitable | resident |
Altitude | 0 - 1150 m | Occasional altitudinal limits | (max) 1500 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | 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 | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Residential & commercial development | Commercial & industrial areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Grey-cheeked Bulbul Alophoixus tephrogenys. Downloaded from
https://datazone.birdlife.org/species/factsheet/grey-cheeked-bulbul-alophoixus-tephrogenys 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.