Taxonomic note
This species was initially considered a subspecies of A. vaughani; unlike the latter (which does not sing), however, it is a good singer, and differs also in measurements, in plumage coloration, in showing no tendency towards leucism, and in DNA (Cibois et al. 2011a). Two subspecies are recognized.
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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2024 | Least Concern | |
2016 | Near Threatened | B1b(v); D2 |
2012 | Near Threatened | B1ab(v);D2 |
2008 | Near Threatened | D2 |
2004 | Near Threatened | |
2000 | Lower Risk/Near Threatened | |
1994 | Lower Risk/Least Concern | |
1988 | Lower Risk/Least Concern |
Migratory status | not a migrant | Forest dependency | low |
Land-mass type | Average mass | 22 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 1,600 km2 | medium |
Area of Occupancy (breeding/resident) | 120 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | stable | poor | suspected | 1998-2008 |
Generation length | 3.1 years | - | - | - |
Number of subpopulations | 2 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The global population size has not been quantified, but the species is described as common across both islands in its range (McCormack 1997, del Hoyo et al. 2006, Thibault and Cibois 2017, eBird 2023).
Trend justification: There are no data on population trends. Although introduced species and habitat loss and fragmentation are plausible threats, the species occurs in a wide variety of habitats and seemingly remains very common throughout both islands. Additionally, forests on Mangaia have been regenerating in spite of these threats, with forest extent (primarily secondary forest, but also primary and Barringtonia forests) substantially increasing between 1996 and 2019 due to the cessation of widespread pineapple cultivation (Thacker et al. 2022). eBird records on Mangaia also do not suggest the species has become substantially less common (eBird 2023). In the absence of evidence for any declines or substantial threats, the species is here suspected to be stable.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Cook Islands | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Cook Islands | Mangaia |
Cook Islands | Miti'aro Island |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Rural Gardens | suitable | resident |
Forest | Subtropical/Tropical Moist Lowland | suitable | resident |
Shrubland | Subtropical/Tropical Moist | suitable | resident |
Wetlands (inland) | Bogs, Marshes, Swamps, Fens, Peatlands | suitable | resident |
Altitude | 0 - 180 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%) | No decline | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Acridotheres tristis | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | No decline | Low Impact: 5 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Capra hircus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rattus exulans | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rattus rattus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Cook Islands Reed-warbler Acrocephalus kerearako. Downloaded from
https://datazone.birdlife.org/species/factsheet/cook-islands-reed-warbler-acrocephalus-kerearako 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.