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.
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2021 | 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 | low |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 3,450,000 km2 | |
Extent of Occurrence (non-breeding) | 7,290,000 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 200000-667000 mature individuals | poor | suspected | 2009 |
Population trend | stable | - | suspected | - |
Generation length | 3.53 years | - | - | - |
Population justification: The global population is estimated to number > c.1,000,000 individuals (Ferguson-Lees et al. 2001), while national population estimates include: c.100-10,000 breeding pairs and c.50-1,000 individuals on migration in China; c.100-10,000 breeding pairs and < c.50 individuals on migration in Korea; < c.50 individuals on migration in Japan and c.100-10,000 breeding pairs and c.50-1,000 individuals on migration in Russia (Brazil 2009). A national census in South Africa recorded 111,291 individuals in 2009 (Symes and Woodborne 2010), which led to a global population estimate of 300,000-500,000 individuals (A. van Zyl, cited in Global Raptor Information Network 2015). This suggests that either a large proportion of the population overwinters further north or that the global population size is considerably smaller than the maximum estimate of 1,000,000 individuals (Symes and Woodborne 2010). It is placed in the band 300,000-1,000,000 individuals, roughly equating to 200,000-667,000 mature individuals.
Trend justification: The population is suspected to historically have undergone rapid declines due to persecution along its migration route. However, thanks to a successful community outreach project in Nagaland, India, there have been no reports of hunting in the area since 2013. The population is now suspected to be stable in the absence of evidence for any declines or substantial threats.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Angola | extant | native | yes | |||
Bangladesh | extant | native | yes | |||
Bhutan | extant | native | yes | |||
Botswana | extant | native | yes | |||
Burundi | extant | native | yes | |||
China (mainland) | extant | native | yes | yes | ||
Congo, The Democratic Republic of the | extant | vagrant | ||||
Eswatini | extant | native | yes | |||
Ethiopia | extant | native | yes | |||
Hong Kong (China) | extant | vagrant | yes | |||
India | extant | native | yes | |||
Italy | extant | vagrant | ||||
Japan | extant | vagrant | ||||
Kenya | extant | native | yes | |||
Laos | extant | native | yes | |||
Lesotho | extant | native | yes | |||
Malawi | extant | native | yes | |||
Maldives | extant | native | yes | |||
Mongolia | extant | native | yes | |||
Mozambique | extant | native | yes | yes | ||
Myanmar | extant | native | yes | |||
Namibia | extant | native | yes | |||
Nepal | extant | native | yes | |||
North Korea | extant | native | yes | yes | ||
Northern Mariana Islands (to USA) | extant | vagrant | ||||
Oman | extant | native | yes | |||
Pakistan | extant | vagrant | yes | |||
Qatar | extant | vagrant | yes | |||
Russia | extant | native | yes | |||
Russia (Asian) | extant | native | yes | |||
Rwanda | extant | native | yes | |||
Saudi Arabia | extant | vagrant | yes | |||
Seychelles | extant | vagrant | ||||
Somalia | extant | native | yes | |||
South Africa | extant | native | yes | |||
South Korea | extant | native | yes | |||
Sri Lanka | extant | native | yes | |||
St Helena (to UK) | extant | vagrant | ||||
Tanzania | extant | native | yes | |||
Thailand | extant | native | yes | |||
Uganda | extant | native | yes | |||
United Arab Emirates | extant | vagrant | yes | |||
Vietnam | extant | native | yes | |||
Yemen | extant | native | yes | |||
Zambia | extant | native | yes | |||
Zimbabwe | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Botswana | Okavango Delta |
India | Dailong Rongku Forest |
India | Doyang Reservoir and Pangti Forest |
India | Habang |
India | Krungming Reserve Forest, Khorongma & Kopili-Umrangsu Reservoirs |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Arable Land | suitable | non-breeding |
Artificial/Terrestrial | Plantations | suitable | non-breeding |
Forest | Temperate | suitable | breeding |
Grassland | Subtropical/Tropical Dry | suitable | non-breeding |
Grassland | Temperate | suitable | breeding |
Savanna | Dry | suitable | non-breeding |
Wetlands (inland) | Bogs, Marshes, Swamps, Fens, Peatlands | suitable | breeding |
Altitude | Occasional altitudinal limits | (max) 4420 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Shifting agriculture | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Majority (50-90%) | Rapid Declines | Past Impact | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Natural system modifications | Other ecosystem modifications | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Amur Falcon Falco amurensis. Downloaded from
https://datazone.birdlife.org/species/factsheet/amur-falcon-falco-amurensis 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.