Taxonomic note
Dicrurus hottentottus, D. palawanensis (Handbook of the Birds of the World and BirdLife International 2023) and D. striatus (del Hoyo and Collar 2016) were previously lumped as D. hottentottus following a previous split of D. mengai from D. hottentottus, acknowledged by Rocamora and Yeatman-Berthelot (2009). Formerly considered conspecific with D. sumatranus, D. densus, D. menagei, D. montanus and D. bracteatus. Vocal analysis (Boesman 2016) reveals that evaluation of vocal differences in this group is very difficult as vocabulary of each group (including mimicry) appears to be even wider than already known. Subspecies banggaiensis sometimes synonymized with pectoralis or leucops, and seems closer to latter. Clinal decrease in size from N to S, birds in C India being similar to those of Myanmar and Thailand, intermediate between those of Himalayan foothills and those of S India (extreme length of male tail 149–164 mm in Himalayas, 132–155 in C India, 114–128 in SW India). Nominate subspecies intergrades with brevirostris from S China (W Yunnan) and N Myanmar E to N Vietnam. Proposed subspecies chrishna (Nepal foothills), allegedly larger than specimens from C and S India, appears indistinguishable from nominate; termeuleni (Jakarta Bay, in W Java) considered inseparable from jentincki, but further study required. Ten subspecies currently recognized.
Taxonomic source(s)
Handbook of the Birds of the World and BirdLife International. 2023. Handbook of the Birds of the World and BirdLife International digital checklist of the birds of the world. Version 8. Available at: https://datazone.birdlife.org/userfiles/file/Species/Taxonomy/HBW-BirdLife_Checklist_v8_Dec23.zip.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2023 | Least Concern | |
2016 | Not Recognised | |
2012 | Not Recognised | |
2008 | Not Recognised | |
2004 | Not Recognised | |
2000 | Not Recognised | |
1994 | Not Recognised | |
1988 | Not Recognised |
Migratory status | full migrant | Forest dependency | medium |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 22,500,000 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | decreasing | - | suspected | 2017-2027 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Generation length | 3.52 years | - | - | - |
Number of subpopulations | 10-100 | - | - | - |
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 fairly common to uncommon (Grimmett et al. 1998, Rocamora et al. 2020, Eaton et al. 2021).
Trend justification: The population is suspected to be declining slowly due to habitat loss within its range. In the three generations to 2022, forest cover loss in its range was c.9% (Global Forest Watch 2023, based on Hansen et al. [2013] and methods disclosed therein) and this is thought to be ongoing. However, the species also occurs in secondary growth, dense scrub and forest edge, and it is also reportedly tolerant of degraded forest and plantations; it is therefore unlikely to be declining particularly rapidly. Trapping for the Indonesian songbird trade has also been identified as a threat, with the species appearing in low numbers on physical market survey inventories (Chng et al. 2016, 2018) and online marketplace platforms (Okarda et al. 2022), though this is thought unlikely to be causing significant reductions in global population size. Declines are here placed in the range 1-9% in three generations.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Bangladesh | extant | native | yes | |||
Bhutan | extant | native | yes | yes | ||
Brunei | extant | native | yes | |||
Cambodia | extant | native | yes | yes | ||
China (mainland) | extant | native | yes | yes | ||
India | extant | native | yes | yes | ||
Indonesia | extant | native | yes | |||
Laos | extant | native | yes | yes | ||
Malaysia | extant | native | yes | |||
Myanmar | extant | native | yes | yes | ||
Nepal | extant | native | yes | yes | ||
Philippines | extant | native | yes | |||
Thailand | extant | native | yes | yes | ||
Vietnam | extant | native | yes | yes |
Country/Territory | IBA Name |
---|
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 | suitable | resident |
Forest | Subtropical/Tropical Moist Montane | suitable | resident |
Altitude | 0 - 2200 m | Occasional altitudinal limits | (max) 2400 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 | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
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 | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | national |
Recommended citation
BirdLife International (2024) Species factsheet: Hair-crested Drongo Dicrurus hottentottus. Downloaded from
https://datazone.birdlife.org/species/factsheet/hair-crested-drongo-dicrurus-hottentottus on 11/12/2024.
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 11/12/2024.