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 |
---|---|---|
2021 | Near Threatened | A2cd+4cd |
2016 | Near Threatened | C1 |
2012 | Near Threatened | C1 |
2008 | Near Threatened | C1 |
2004 | Near Threatened | |
2000 | Lower Risk/Near Threatened | |
1994 | Lower Risk/Least Concern | |
1988 | Lower Risk/Least Concern |
Migratory status | not a migrant | Forest dependency | medium |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 112,500 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | decreasing | poor | inferred | 2002-2022 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 10-19% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 10-25% | - | - | - |
Generation length | 6.6 years | - | - | - |
Population justification: The global population size has not been quantified, but the species is described as generally fairly scarce, although common on Tanahjampea, Tanimbar, Wetar and Karimunjawa islands (Gibbs et al. 2001, Trainor et al. 2009, Susanto 2012, B. van Balen in litt. 2016, C. Trainor & J. P. Lopez in litt. 2020), 'uncommon' on Babar and 'fairly frequent' at secondary forest edges on Sermata (Trainor and Verbelen 2013). Across Timor it appears to have declined sharply due to intensive hunting (C. Trainor & J. P. Lopez in litt. 2020).
In West Timor there are now only very low numbers at Bipolo and Camplong, where previously large flocks could be easily observed. Similarly, in Timor-Leste numbers encountered in Nino Konis Santana National Park in 2019 were far lower than previously, with the decline ascribed to hunting occurring throughout Timor (C. Trainor & J. P. Lopez 2020). The species is now locally absent from many formerly occupied sites in the country, and is even greatly reduced in the Oecusse enclave (C. Trainor & J. P. Lopez in litt. 2020).
Trend justification: Hunting and habitat degradation are suspected to be driving a moderate decline overall, but rapid declines have occurred due solely to hunting in Timor-Leste and West Timor in recent years (C. Trainor & J. P. Lopez in litt. 2020). The species has declined from being common in forested sites (Bipolo and Camplong in West Timor, Nino Konis Santana National Park in Timor-Leste) at the start of the 2000s to only being recording in ones and twos in 2019 (C. Trainor & J. P. Lopez in litt. 2020). Should the impact of hunting be mitigated, there is the potential for considerable future recovery in the depleted parts of the range.
On many of the small islands on which the species occurs numbers remain good. The stronghold of the species may now be Wetar where there continue to be counts of large flocks and a large proportion of forest remains including favoured riparian Canarium groves (Trainor et al. 2009, C. Trainor & J. P. Lopez in litt. 2020).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Indonesia | extant | native | yes | |||
Timor-Leste | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Indonesia | Bipolo |
Indonesia | Camplong |
Indonesia | Gunung Arnau |
Indonesia | Kepulauan Lemola |
Indonesia | Kepulauan Tayandu |
Indonesia | Oenasi |
Indonesia | Pegunungan Daab - Boo |
Indonesia | Pulau Babar |
Indonesia | Pulau Besar |
Indonesia | Pulau Damar |
Indonesia | Pulau Kalatoa |
Indonesia | Pulau Manuk |
Indonesia | Pulau Romang |
Indonesia | Pulau Selayar |
Indonesia | Pulau Tana Jampea |
Timor-Leste | Areia Branca no Dolok Oan |
Timor-Leste | Atauro Island |
Timor-Leste | Be Malae |
Timor-Leste | Fatumasin |
Timor-Leste | Irabere - Iliomar |
Timor-Leste | Jaco Island |
Timor-Leste | Lore |
Timor-Leste | Maubara |
Timor-Leste | Monte Mak Fahik - Sarim |
Timor-Leste | Mount Paitchau and Lake Iralalaro |
Timor-Leste | Subaun |
Timor-Leste | Sungai Klere |
Timor-Leste | Tasitolu |
Timor-Leste | Tilomar |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Plantations | suitable | resident |
Forest | Subtropical/Tropical Mangrove Vegetation Above High Tide Level | suitable | resident |
Forest | Subtropical/Tropical Moist Lowland | suitable | resident |
Shrubland | Subtropical/Tropical Moist | suitable | resident |
Altitude | 0 - 930 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 | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Rapid Declines | Medium Impact: 6 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Residential & commercial development | Tourism & recreation areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Transportation & service corridors | Roads & railroads | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Pink-headed Imperial-pigeon Ducula rosacea. Downloaded from
https://datazone.birdlife.org/species/factsheet/pink-headed-imperial-pigeon-ducula-rosacea 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.