EN
Waigeo Brushturkey Aepypodius bruijnii



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
- B1ab(iii)+2ab(iii) B1ab(iii)+2ab(iii); D1

Red List history
Year Category Criteria
2021 Endangered B1ab(iii)+2ab(iii)
2016 Endangered B1ab(ii,iii,v)+2ab(ii,iii,v); C2a(ii)
2012 Endangered B1ab(ii,iii,v)+2ab(ii,iii,v);C2a(ii)
2008 Endangered B1a+b(ii,iii); B2a+b(ii,iii); C2a(ii)
2005 Vulnerable
2004 Vulnerable
2000 Vulnerable
1996 Vulnerable
1994 Vulnerable
1988 Threatened
Species attributes

Migratory status not a migrant Forest dependency high
Land-mass type shelf island
Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 784 km2 medium
Area of Occupancy (breeding/resident) 240 km2 medium
Number of locations 3-6,4 -
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 977 mature individuals medium estimated 2003
Population trend decreasing poor suspected 2001-2027
Generation length 8.42 years - - -
Number of subpopulations 1 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: The total population is estimated to number at least 977 mature individuals (Mauro 2006), roughly equivalent to 1,400 individuals in total. It is suspected that the species may no longer occur to the west of Majalibit Bay, which was the only specific location assigned to specimens collected in the first half of the 20th Century. However there is no information on the trend of the population since the investigations at the start of the 20th Century (Mauro 2002, 2005, 2006). There continue to be sightings on Mt Danai and occasional records of presumed wandering immatures and possibly non-breeders at lower levels (eBird 2020). The observations of these apparently dispersing individuals suggests that it is appropriate to assume there is a single connected population, although confirmation of this is desirable. However, Mauro (2006) found that these records were very rare and never pertained to birds with adult male plumage, and indeed appeared to be related to movements during drought periods and should be considered as extralimital sightings. However, if it were to be demonstrated that there is a floating population of mature individuals in areas away from the restricted breeding habitat then the total number of mature individuals may be larger. To date there has been little habitat loss within the altitudinal range of the species and any population impacts of feral dogs or pigs are unquantified, although the latter are suspected to significantly impact reproductive success at least on Mt. Danai (Davies 2008).

Trend justification: The population is suspected to be declining at a slow or moderate rate, owing to hunting, predation by dogs and pigs and habitat loss, particularly from fire.


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

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

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Lowland suitable resident
Forest Subtropical/Tropical Moist Montane major resident
Altitude 620 - 970 m Occasional altitudinal limits (min) 200 m

Threats & impact
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
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Species mortality
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Ecosystem degradation
Climate change & severe weather Droughts Timing Scope Severity Impact
Ongoing Majority (50-90%) Causing/Could cause fluctuations Medium Impact: 6
Stresses
Reduced reproductive success
Climate change & severe weather Habitat shifting & alteration Timing Scope Severity Impact
Future Majority (50-90%) Slow, Significant Declines Low Impact: 4
Stresses
Indirect ecosystem effects, Ecosystem degradation, Reduced reproductive success
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Canis familiaris Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Sus scrofa Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species disturbance, Reduced reproductive success
Natural system modifications Fire & fire suppression - Increase in fire frequency/intensity Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species disturbance, Ecosystem degradation, Reduced reproductive success

Utilisation
Purpose Scale
Food - human subsistence

Recommended citation
BirdLife International (2024) Species factsheet: Waigeo Brushturkey Aepypodius bruijnii. Downloaded from https://datazone.birdlife.org/species/factsheet/waigeo-brushturkey-aepypodius-bruijnii on 18/12/2024.
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 18/12/2024.