Taxonomic source(s)
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 |
---|---|---|
2023 | Least Concern | |
2016 | Near Threatened | B1ab(ii,iii,v);C1 |
2012 | Near Threatened | B1ab(ii,iii,v);C1 |
2008 | Near Threatened | B1a+b(iii,v); C1 |
2004 | Near Threatened | |
2000 | Lower Risk/Near Threatened | |
1994 | Lower Risk/Near Threatened | |
1988 | Near Threatened |
Migratory status | full migrant | Forest dependency | high |
Land-mass type |
shelf island |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 2,150,000 km2 | medium |
Area of Occupancy (breeding/resident) | 8,000 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | stable | poor | suspected | - |
Generation length | 3.95 years | - | - | - |
Number of subpopulations | 3 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The population has not been quantified and an exercise to do so would be greatly hampered by its movements between islands. On islands where the majority of tree cover has been removed it is expectedly rare, but on others it can be quite common (eBird 2022). The population of C. j. nitens has previously been estimated to number 100 in 2014 (Ando et al. 2014) however it is recently reported to be commoner following feral cat control (O. Chikara in litt. 2020).
Trend justification: While the number of recorded sites fell between atlas efforts in 1997-2000 and 2016-2021 (from 25 to 22) (Bird Breeding Distribution Survey Committee 2021) this is not thought to be indicative of global population declines. In the absence of hunting and logging pressures and recent indication that C. j. nitens (which can represent only a small percentage of the global population) is no longer decreasing thanks to conservation effort (O. Chikara in litt. 2022), the population is suspected to be stable.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
China (mainland) | extant | vagrant | ||||
Japan | extant | native | yes | |||
Russia | extant | vagrant | yes | |||
South Korea | extant | native | yes | |||
Taiwan, China | extant | vagrant |
Country/Territory | IBA Name |
---|---|
Japan | Amami islands |
Japan | Aogashima island |
Japan | Chichijima islands |
Japan | Danjo islands |
Japan | Hachijojima island |
Japan | Hahajima islands |
Japan | Kanmurijima and Kutsujima islets |
Japan | Kazan-retto islands |
Japan | Kii Nagashima islets |
Japan | Koshikijima islands |
Japan | Kozushima island |
Japan | Mikurajima island |
Japan | Miyakejima island |
Japan | Mukojima islands |
Japan | Niijima and Shikinejima Islands |
Japan | Oki islands |
Japan | Okinoshima and Koyajima islets |
Japan | Oshima island |
Japan | Seinan islands |
Japan | Tokara islands |
Japan | Toshima island |
Japan | Tsushima islands |
Japan | Yaeyama islands |
Japan | Yakushima and Tanegashima islands |
Japan | Yambaru, northern Okinawa forest |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | breeding |
Forest | Subtropical/Tropical Moist Lowland | major | non-breeding |
Forest | Temperate | major | non-breeding |
Forest | Temperate | major | breeding |
Altitude | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Minority (<50%) | Negligible declines | Past Impact | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Minority (<50%) | Negligible declines | Past Impact | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Problematic native species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
|
|||||||||
Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Japanese Woodpigeon Columba janthina. Downloaded from
https://datazone.birdlife.org/species/factsheet/japanese-woodpigeon-columba-janthina 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.