NT
Biak Gerygone Gerygone hypoxantha



Taxonomy

Taxonomic note

Gerygone magnirostris and G. hypoxantha (del Hoyo and Collar 2016) were previously lumped as G. magnirostris following Christidis & Boles (2008) and Sibley & Monroe (1990, 1993).

 

Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A., Fishpool, L.D.C., Boesman, P. and Kirwan, G.M. 2016. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 2: Passerines. Lynx Edicions and BirdLife International, Barcelona, Spain and Cambridge, UK.
Morony, J. J.; Bock, W. J.; Farrand, J. 1975. Reference list of the birds of the world. Department of Ornithology, American Museum of Natural History, New York.

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

Red List history
Year Category Criteria
2023 Near Threatened B1b(iii)
2016 Vulnerable C2a(ii)
2012 Not Recognised
2008 Not Recognised
2007 Not Recognised
2004 Endangered
2000 Endangered
1994 Endangered
1988 Threatened
Species attributes

Migratory status not a migrant Forest dependency medium
Land-mass type Average mass 7 g
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 3,600 km2
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 15000-45000 mature individuals poor suspected 2022
Population trend decreasing - suspected 2017-2027
Rate of change over the past 10 years/3 generations (longer of the two periods) 1-9% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 1-9% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 1-9% - - -
Generation length 2.92 years - - -
Number of subpopulations 1 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: The population size of this species has not previously been directly quantified. Other species of Gerygone occur at quite high densities (20-400 birds/km2; e.g. Fogden 1976, Bell 1982), although qualitatively G. hypoxantha is considered rare (Pratt and Beehler 2015, Beehler and Pratt 2016), while the limited eBird (2022) data available support that it may occur at lower densities than congeners. Using the global landcover 2 estimate of forest cover for the island (closed to open broadleaved evergreen or semi-deciduous forest) and excluding fragments smaller than 1 km2 results in an area classified as forest habitat of 1,572 km2. Consequently, assuming (somewhat precautionarily) a combined occupancy/density of 10-30 mature individuals/km2, the population is suspected of numbering 15,000-45,000 mature individuals, although there remains high uncertainty with this.

Trend justification: No direct assessment of rate of population change has been made for the species. It is considered to be forest dependent and there has been a slow rate of forest cover loss, up to 4% in the ten years to 2022 (data from Global Forest Watch 2022, using Hansen et al. [2013] data and methods disclosed therein) and this is suspected to be causing broadly equivalent reductions in population size of this species.


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 Dry suitable resident
Forest Subtropical/Tropical Mangrove Vegetation Above High Tide Level major resident
Forest Subtropical/Tropical Moist Lowland suitable resident
Shrubland Subtropical/Tropical Moist suitable resident
Altitude 0 - 600 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Annual & perennial non-timber crops - Shifting agriculture Timing Scope Severity Impact
Ongoing Low Impact: 3
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Low Impact: 3
Stresses
Ecosystem degradation, Ecosystem conversion

Recommended citation
BirdLife International (2024) Species factsheet: Biak Gerygone Gerygone hypoxantha. Downloaded from https://datazone.birdlife.org/species/factsheet/biak-gerygone-gerygone-hypoxantha on 26/12/2024.
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 26/12/2024.