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 |
---|---|---|
- | - | D1 |
Year | Category | Criteria |
---|---|---|
2022 | Vulnerable | D1 |
2016 | Vulnerable | D1+2 |
2012 | Vulnerable | D1+2 |
2008 | Vulnerable | D1; D2 |
2006 | Vulnerable | |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Lower Risk/Least Concern |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 52 km2 | medium |
Area of Occupancy (breeding/resident) | 52 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 300-1500, 650-750 mature individuals | medium | estimated | 2000 |
Population trend | stable | medium | suspected | 1998-2008 |
Generation length | 4.02 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: In 2009, surveys based on distance sampling broadly estimated the population to number c.1,000 individuals (95% CI 440-2,200 individuals), or approximately 650-700 mature individuals (95% CI 300-1,500; Albar et al. 2010). This is congruent with a crude estimation by Thibault and Guyot (1987) of approximately 1,000 individuals.
Trend justification: Although much forest was destroyed during the period 1917-1964 as a result of phosphate mining, the indigenous vegetation has recovered over the last 40 years and it appears that the mining did not change either the distribution or abundance of the species (Holyoak and Thibault 1984, Seitre and Seitre 1991, Thibault and Cibois 2017). Given that other threats are few, and that the species is tolerant of degraded habitat, the population is presumed to be stable.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
French Polynesia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
French Polynesia | Makatea |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Altitude | 0 - 80 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Whole (>90%) | Unknown | Unknown | ||||||
|
|||||||||
Climate change & severe weather | Storms & flooding | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Unknown | Unknown | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Majority (50-90%) | Unknown | Past Impact | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Makatea Fruit-dove Ptilinopus chalcurus. Downloaded from
https://datazone.birdlife.org/species/factsheet/makatea-fruit-dove-ptilinopus-chalcurus on 26/12/2024.
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 26/12/2024.