Taxonomic note
Manucerthia mana (del Hoyo and Collar 2016) was previously placed in the genus Oreomystis 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 |
---|---|---|
- | B1ab(i,ii,iii,v) | A2bce+3bce+4bce; B1ab(i,ii,iii,v)+2ab(i,ii,iii,v); C1; D2 |
Year | Category | Criteria |
---|---|---|
2023 | Endangered | B1ab(i,ii,iii,v) |
2016 | Endangered | B1ab(i,ii,iii,iv,v) |
2013 | Endangered | B1ab(i,ii,iii,iv,v) |
2012 | Endangered | B1ab(i,ii,iii,iv,v) |
2008 | Endangered | B1a+b(i,ii,iii,iv,v) |
2004 | Endangered | |
2000 | Endangered | |
1996 | Endangered | |
1994 | Endangered | |
1988 | Near Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | 15 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 4,200 km2 | medium |
Area of Occupancy (breeding/resident) | 1,172 km2 | |
Number of locations | 1 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 9300 mature individuals | medium | estimated | 2009 |
Population trend | decreasing | poor | estimated | 2017-2027 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 20-40% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 20-40% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 20-40% | - | - | - |
Generation length | 3.31 years | - | - | - |
Number of subpopulations | 4 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: Surveys in 1976-1983 estimated the population at c.12,500 individuals (Scott et al. 1986). In 2009, the total population was estimated at c.14,000 birds (Gorresen et al. 2009), roughly equivalent to 9,300 mature individuals overall, with 9,888 birds (95% CI: 6,115-14,974) occurring in Hakalau Forest National Wildlife Refuge (Kendall et al. 2022).
Trend justification: Trend analysis has previously indicated a density increase in Hakalau Forest National Wildlife Refuge in north windward Hawai‘i (Camp et al. 2010b, 2016) and the species was considered stable overall (USWFS 2020). However, a more recent analysis of annual population density estimates in this area showed an overall downwards trend in the time period 1987-2019 and in the most recent decade 2010-2019, with this region supporting 71% of the global population (Kendall et al. 2022). In the period 2010-2019, density across all strata (open forest, closed forest and pasture) decreased by approximately 20%, with density in closed forest alone declining by approximately 40% (Kendall et al. 2022). The ongoing rate of decline is therefore placed in the range 20-40% within ten years. Additionally, trend analysis has shown that density for central windward Hawai‘i is declining in intact native forest (Camp et al. 2010a), while trends are unclear for Ka‘? and populations in central Kona and Hual?lai regions are thought to be very small or nearly extirpated (Gorresen et al. 2009, USWFS 2020). Declines are predicted to continue given that the threats are ongoing. Given that the species is highly susceptible to avian malaria, climate change is likely to reduce the area of suitable remaining habitat and drive further declines through causing an increase in the elevation below which regular transmission occurs (USWFS 2020).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
USA | extant | native | yes |
Country/Territory | IBA Name |
---|---|
USA | Hamakua Forests |
USA | Kau Forest |
USA | Kona Forests |
USA | Mauna Loa-Kilauea Forests |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Dry | major | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 1500 - 1900 m | Occasional altitudinal limits | 1000 - 2300 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or 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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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 - Rattus rattus | 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 - Sus domesticus | 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 - Zosterops japonicus | 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 | Problematic species/disease of unknown origin - Named species | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Negligible declines | Unknown | ||||||
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Invasive and other problematic species, genes & diseases | Viral/prion-induced diseases - Avipoxvirus | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
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Recommended citation
BirdLife International (2024) Species factsheet: Hawaii Creeper Manucerthia mana. Downloaded from
https://datazone.birdlife.org/species/factsheet/hawaii-creeper-manucerthia-mana on 27/11/2024.
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 27/11/2024.