Taxonomic source(s)
AERC TAC. 2003. AERC TAC Checklist of bird taxa occurring in Western Palearctic region, 15th Draft. Available at: http://www.aerc.eu/DOCS/Bird_taxa_of_the_WP15.xls.
Cramp, S. and Simmons, K.E.L. (eds). 1977-1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. Oxford University Press, Oxford.
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 |
---|---|---|
2024 | Least Concern | |
2016 | Least Concern | |
2012 | Least Concern | |
2009 | Least Concern | |
2008 | Least Concern | |
2004 | Least Concern | |
2000 | Lower Risk/Least Concern | |
1994 | Lower Risk/Least Concern | |
1988 | Lower Risk/Least Concern |
Migratory status | full migrant | Forest dependency | medium |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 37,700,000 km2 | |
Extent of Occurrence (non-breeding) | 17,800,000 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | decreasing | - | suspected | - |
Generation length | 2.13 years | - | - | - |
Population justification: The population size is unknown, but the species is described as common to locally common in much of its range (del Hoyo et al. 2006), while national population estimates include: c.10,000-100,000 breeding pairs and c.1,000-10,000 individuals on migration in China; c.50-1,000 individuals on migration and < c.50 wintering individuals in Taiwan; c.10,000-100,000 breeding pairs and c.1,000-10,000 individuals on migration in Korea; c.100-100,000 breeding pairs and c.50-10,000 individuals on migration in Japan and c.10,000-100,000 breeding pairs and c.1,000-10,000 individuals on migration in Russia (Brazil 2009). This species is considered to have a medium dependency on forest habitat, and tree cover is estimated to have declined by 11.2% within its mapped range over the past 10 years (Global Forest Watch 2022, using Hansen et al. [2013] data and methods disclosed therein). Therefore, as a precautionary measure, it is tentatively suspected that this loss of cover may have led to a decline of between 1-19% in the species' population size over the same time frame.
Trend justification: .
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Bhutan | extant | native | yes | |||
Brunei | extant | native | yes | |||
Cambodia | extant | native | yes | |||
China (mainland) | extant | native | yes | |||
Denmark | extant | vagrant | ||||
Finland | extant | vagrant | ||||
Greece | extant | vagrant | ||||
Hong Kong (China) | extant | native | ||||
India | extant | native | yes | |||
Indonesia | extant | native | yes | |||
Japan | extant | native | yes | |||
Laos | extant | native | yes | |||
Macao (China) | extant | native | ||||
Malaysia | extant | native | yes | |||
Mongolia | extant | native | yes | |||
Myanmar | extant | native | yes | |||
Nepal | extant | native | yes | |||
North Korea | extant | native | yes | |||
Oman | extant | vagrant | yes | |||
Philippines | extant | native | yes | |||
Russia | extant | native | yes | |||
Russia (Asian) | extant | native | yes | |||
Russia (Central Asian) | extant | native | yes | |||
Singapore | extant | native | yes | |||
South Korea | extant | native | yes | |||
Sri Lanka | extant | native | yes | |||
Sweden | extant | vagrant | ||||
Taiwan, China | extant | native | yes | |||
Tajikistan | extant | native | yes | |||
Thailand | extant | native | yes | |||
USA | extant | vagrant | ||||
Vietnam | extant | native | yes |
Country/Territory | IBA Name |
---|
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Plantations | suitable | non-breeding |
Artificial/Terrestrial | Plantations | suitable | breeding |
Artificial/Terrestrial | Rural Gardens | suitable | non-breeding |
Artificial/Terrestrial | Rural Gardens | suitable | breeding |
Artificial/Terrestrial | Urban Areas | suitable | non-breeding |
Artificial/Terrestrial | Urban Areas | suitable | breeding |
Forest | Subtropical/Tropical Mangrove Vegetation Above High Tide Level | suitable | non-breeding |
Forest | Subtropical/Tropical Mangrove Vegetation Above High Tide Level | suitable | breeding |
Forest | Subtropical/Tropical Moist Lowland | suitable | non-breeding |
Forest | Subtropical/Tropical Moist Lowland | suitable | breeding |
Forest | Subtropical/Tropical Moist Montane | suitable | non-breeding |
Forest | Subtropical/Tropical Swamp | suitable | non-breeding |
Forest | Temperate | suitable | breeding |
Altitude | 0 - 2340 m | Occasional altitudinal limits |
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Asian Brown Flycatcher Muscicapa dauurica. Downloaded from
https://datazone.birdlife.org/species/factsheet/asian-brown-flycatcher-muscicapa-dauurica 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.