Taxonomic note
Copsychus saularis and C. mindanensis (del Hoyo and Collar 2016) were previously lumped as C. saularis 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 |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2021 | Least Concern | |
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 | 36 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 19,500,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | stable | - | suspected | - |
Generation length | 2.4 years | - | - | - |
Population justification: The global population size has not been quantified, but the species is described as common (del Hoyo et al. 2005), while national population sizes have been estimated at c.10,000-1,000,000 breeding pairs in China and < c.10,000 introduced breeding pairs in Taiwan (Brazil 2009). During the ‘Big Month’ citizen science event (conducted in January 2020 comprising 22,054 checklists) across Java and Bali however, the species was recorded in just 9 (0.11%) of the 7,935 tetrads (2 × 2 km squares) visited (T. Squires and S. Marsden in litt. 2020). The species is thus considered rarer across some Southeast Asian sites (Collar et al. 2020).
Trend justification: The species may be subjected to some level of exploitation across parts of its range. Subspecies amoenus is for example only thought to survive in shaded, and well-protected areas of resorts in Bali, and although found in captivity, the species is thought to be in critical status (F. Rheindt in litt. 2020). In Singapore, the species had moreover undergone previous declines owed to poaching, habitat loss and competition with native species (Collar et al. 2020). However, although rarer at some sites, due to its commonality throughout most of its range, the overall population is suspected to be stable in the absence of evidence for any precipitous declines.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Bangladesh | extant | native | yes | |||
Bhutan | extant | native | yes | |||
Brunei | extant | native | yes | |||
Cambodia | extant | native | yes | |||
China (mainland) | extant | native | yes | |||
India | extant | native | yes | |||
Indonesia | extant | native | yes | |||
Laos | extant | native | yes | |||
Malaysia | extant | native | yes | |||
Myanmar | extant | native | yes | |||
Nepal | extant | native | yes | |||
Pakistan | extant | native | yes | |||
Singapore | extant | native | yes | |||
Sri Lanka | extant | native | yes | |||
Taiwan, China | extant | introduced | yes | |||
Thailand | extant | native | yes | |||
Vietnam | extant | native | yes |
Country/Territory | IBA Name |
---|
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Arable Land | suitable | resident |
Artificial/Terrestrial | Plantations | suitable | resident |
Artificial/Terrestrial | Rural Gardens | suitable | resident |
Forest | Subtropical/Tropical Dry | suitable | resident |
Forest | Subtropical/Tropical Mangrove Vegetation Above High Tide Level | suitable | resident |
Forest | Subtropical/Tropical Moist Lowland | suitable | resident |
Forest | Subtropical/Tropical Moist Montane | suitable | resident |
Forest | Subtropical/Tropical Swamp | suitable | resident |
Shrubland | Subtropical/Tropical Moist | suitable | resident |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | suitable | resident |
Altitude | 0 - 1900 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Agro-industry farming | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
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 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Problematic native species/diseases | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Oriental Magpie-robin Copsychus saularis. Downloaded from
https://datazone.birdlife.org/species/factsheet/oriental-magpie-robin-copsychus-saularis 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.