NT
Yellowish Imperial-pigeon Ducula subflavescens



Taxonomy

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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - -

Red List history
Year Category Criteria
2021 Near Threatened A3c+4c
2016 Near Threatened A2c+3c+4c
2012 Near Threatened A2c+3c+4c
2008 Near Threatened A2c; A3c; A4c
2004 Near Threatened
2000 Lower Risk/Near Threatened
1994 Lower Risk/Least Concern
1988 Lower Risk/Least Concern
Species attributes

Migratory status nomadic Forest dependency high
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 254,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 38000 - 249000 mature individuals poor suspected 2021
Population trend decreasing poor inferred 2020-2041
Rate of change over the past 10 years/3 generations (longer of the two periods) 6-16% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 12-25% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 12-25% - - -
Generation length 6.97 years - - -
Number of subpopulations 2-20 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: No population density estimates are available, but the population size is suspected to be greater than 10,000 mature individuals (Buchanan et al. 2008; Davis et al. 2018). The species has been recorded frequently during surveys on New Britain, although the frequent records in hill forests may have resulted from the species's tendency to fly large distances, and may obscure a dependency on coastal and riparian habitats (Davis et al. 2018).

The species has a large range, with an estimated 39,000 kmof tree cover with at least 50% canopy cover within its range in 2010, although this figure is likely to include oil palm plantations (Global Forest Watch 2021). Based on the first quartile and median recorded densities of congeners (14.5 and 38 individuals/km2, respectively), the area of tree cover stated above, and assuming that 10-25% of available tree cover is occupied, the population size is tentatively suspected to fall in the range 57,000 - 373,000 individuals, roughly equating to 38,000 - 249,000 mature individuals.

The subpopulation structure is not known, but the species has a fairly high dispersal ability, and occurs on a large number of islands. The number of subpopulations is suspected to fall within the range 2-20.

Trend justification: Over 19 years from 2000 to 2019, approximately 9.6% of tree cover with at least 50% canopy cover was lost from across the species's range (Global Forest Watch 2021). Extrapolating over 21 years (three generations), an estimated 11% of tree cover was lost from the species's range, and 12% is suspected to be lost over the next three generations. However, the estimated rate of tree cover loss was higher over the past few years, particularly in 2015 (Global Forest Watch 2021). Based on the rate of tree cover loss over the period 2014-2019 alone, it may be suspected that 20% of tree cover will be lost over the next three generations.
The impact of forest loss and degradation on the species is not known, and the species may experience declines as a result of forest degradation in addition to forest loss (Buchanan et al. 2008), although it has been recorded in high numbers in degraded forest (Davis et al. 2018). The population is therefore suspected to have undergone a reduction of 6-16% over the past three generations, and it is suspected to undergo a reduction of 7-25% over the next three generations.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Papua New Guinea extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Terrestrial Subtropical/Tropical Heavily Degraded Former Forest suitable resident
Forest Subtropical/Tropical Moist Lowland major resident
Altitude 0 - 940 m Occasional altitudinal limits  

Threats & impact
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%) Rapid Declines Medium Impact: 6
Stresses
Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion

Recommended citation
BirdLife International (2024) Species factsheet: Yellowish Imperial-pigeon Ducula subflavescens. Downloaded from https://datazone.birdlife.org/species/factsheet/yellowish-imperial-pigeon-ducula-subflavescens on 23/11/2024.
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 23/11/2024.