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 |
---|---|---|
- | - | C2a(ii) |
Year | Category | Criteria |
---|---|---|
2024 | Vulnerable | C2a(ii) |
2016 | Vulnerable | C2a(ii) |
2012 | Vulnerable | C2a(ii) |
2008 | Vulnerable | C2a(ii) |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 9,870 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 5600-6000 mature individuals | medium | estimated | 2023 |
Population trend | decreasing | poor | inferred | 2018-2030 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 5-10% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 5-10% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 5-10% | - | - | - |
Generation length | 4.03 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: This species is described as uncommon in primary and secondary forest patches (Eaton et al. 2021). Fieldwork in 1989 and 1992 yielded density estimates of 6.9 (±1.2) birds per km2 (Jones et al. 1995). Given 1,080 km2 of closed-canopy forest on Sumba, this was extrapolated and corrected upwards to a global population estimate of 9,100 birds (Jones et al. 1995), roughly equivalent to c.6,000 mature individuals. Given nearly 30 years has passed since the creation of this estimate, it is in need of confirmation; however assuming the rate of forest loss since this time is axiomatic with population declines, it may have declined by c.6% since. Consequently, it is now estimated to number 5,600-6,000 mature individuals.
Trend justification: Though it may be partially tolerant of degradation, as a forest-dependent species it is suspected to be in decline owing to ongoing habitat loss within its range. Forest cover extent in this species' range reduced by c. 6% overall in the three generations to 2022 (Global Forest Watch 2023, based on data from Hansen et al. [2013] and methods disclosed therein), and based on losses in 2018-2022 this has accelerated slightly to an equivalent rate of c. 7% in three generations. Hunting is a potential additional threat, though this remains unconfirmed. Tentatively, declines are placed in the range 5-10% in three generations and this is suspected to continue.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Indonesia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Indonesia | Laiwanggi Wanggameti |
Indonesia | Luku Melolo |
Indonesia | Manupeu Tanadaru |
Indonesia | Poronumbu |
Indonesia | Tanjung Ngunju |
Indonesia | Yawila |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | suitable | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 160 - 500 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or 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%) | Unknown | Unknown | ||||||
|
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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 | ||||||
|
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Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Red-naped Fruit-dove Ptilinopus dohertyi. Downloaded from
https://datazone.birdlife.org/species/factsheet/red-naped-fruit-dove-ptilinopus-dohertyi on 23/12/2024.
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 23/12/2024.