Taxonomic note
Chlorodrepanis stejnegeri (del Hoyo and Collar 2016) was previously placed in the genus Hemignathus and listed as H. kauaiensis following AOU (1998 & supplements); 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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | A2bce+3bce+4bce; B1ab(i,ii,iii,v)+2ab(i,ii,iii,v); C1+2a(ii) | A2bce+3bce+4bce; B1ab(i,ii,iii,v)+2ab(i,ii,iii,v); C1+2a(ii); D2 |
Year | Category | Criteria |
---|---|---|
2023 | Endangered | A2bce+3bce+4bce; B1ab(i,ii,iii,v)+2ab(i,ii,iii,v); C1+2a(ii) |
2016 | Vulnerable | D2 |
2012 | Vulnerable | D2 |
2008 | Vulnerable | D2 |
2004 | Vulnerable | |
2000 | Vulnerable | |
1994 | Vulnerable | |
1988 | Lower Risk/Least Concern |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 356 km2 | medium |
Area of Occupancy (breeding/resident) | 356 km2 | |
Number of locations | 1 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 2200-4400 mature individuals | medium | estimated | 2022 |
Population trend | decreasing | medium | estimated | 2016-2026 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 55-70% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 55-70% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 55-70% | - | - | - |
Generation length | 2.66 years | - | - | - |
Number of subpopulations | 1-2,1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 99-100, 100% | - | - | - |
Population justification: Surveys in 2018 placed the population at 6,987 individuals (95% CI: 4,672–9,183) (Paxton et al. 2020), roughly equivalent to 3,100-6,100 mature individuals overall. Assuming declines have continued at the same rate (the most recent population estimate suggests an overall decline of c.57% within the time period 2008-2018 [Paxton et al. 2020]), this would now place the population in the band 2,200-4,400 mature individuals. There is also thought to be a small, isolated population in the Makaleha Mountains (Camp et al. 2009), however this is precautionarily assumed not to host mature individuals given the lack of recent records.
Trend justification: During 1968-1973, surveys estimated the population at 10,743 (± 970 standard error), with 76% of the population in the "west of Alaka`i" study compartment (USFWS 1983). Subsequent population estimates suggested that the population was greater than 15,000, possibly up to 20,000 birds, and increasing (Scott et al. 1986, Jacobi and Atkinson 1995, Lindsey et al. 1998). In 1992, Hurricane Iniki devastated forests throughout Kaua`i and all bird populations on the island appeared to have been drastically reduced (Pratt 1993, 1994). Subsequent population estimates suggested that this species had recovered (Jacobi and Atkinson 1995, Lindsey et al. 1998, P. Donaldson in litt. 1999, Foster et al. 2004), with the estimated population in the Alaka`i and Kôke`e areas increasing significantly to around 42,000 individuals in 2000 (Foster et al. 2004). However, estimates in 2012 indicated dramatic declines since 2000 of 91% in the core range and 98% in the periphery, with a resultant population estimate of only 6,519 individuals (95% CI: 4,844– 8,495; Paxton et al. 2016). The most recent population estimate of 6,987 individuals suggests an overall decline of c.57% within the time period 2008-2018 (Paxton et al. 2020), with declines exceeding 60% in interior forest. As such, the rate of decline is placed here in the range 55-70% within ten years.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
USA | extant | native | yes |
Country/Territory | IBA Name |
---|---|
USA | Kauai Forests and Uplands |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 600 - 1600 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Agro-industry farming | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
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Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
|
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Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Slow, Significant Declines | Medium Impact: 7 | ||||||
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Climate change & severe weather | Storms & flooding | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Whole (>90%) | Rapid Declines | Past Impact | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Capra hircus | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Ceratocystis fimbriata | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Named species | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Plasmodium relictum | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Sus scrofa | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Unspecified species | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Unspecified species | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
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Invasive and other problematic species, genes & diseases | Viral/prion-induced diseases - Avipoxvirus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
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Recommended citation
BirdLife International (2024) Species factsheet: Kauai Amakihi Chlorodrepanis stejnegeri. Downloaded from
https://datazone.birdlife.org/species/factsheet/kauai-amakihi-chlorodrepanis-stejnegeri on 24/12/2024.
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 24/12/2024.