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 |
---|---|---|
- | B1ab(iii)+2ab(iii) | B1ab(iii)+2ab(iii); D1 |
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 |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
shelf island |
Average mass | - |
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 | - |
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 | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Indonesia | extant | native | yes |
Country/Territory | IBA Name |
---|
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 |
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 | ||||||
|
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Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Climate change & severe weather | Droughts | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Causing/Could cause fluctuations | Medium Impact: 6 | ||||||
|
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Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Slow, Significant Declines | Low Impact: 4 | ||||||
|
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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 | ||||||
|
|||||||||
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 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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.