CR
Puaiohi Myadestes palmeri



Taxonomy

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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
B1ab(iii) B1ab(iii)+2ab(iii) B1ab(iii)+2ab(iii); D1+2

Red List history
Year Category Criteria
2023 Critically Endangered B1ab(iii)
2016 Critically Endangered B1ab(iii)
2015 Critically Endangered B1ab(iii)
2013 Critically Endangered B1ab(iii)
2012 Critically Endangered B1ab(iii)
2009 Critically Endangered B1a+b(iii)
2008 Critically Endangered
2004 Critically Endangered
2000 Critically Endangered
1996 Critically Endangered
1994 Critically Endangered
1988 Threatened
Species attributes

Migratory status not a migrant Forest dependency high
Land-mass type Average mass 40 g
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 52 km2 medium
Area of Occupancy (breeding/resident) 52 km2
Number of locations 1 -
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 414-580 mature individuals good estimated 2013
Population trend stable medium suspected -
Generation length 3.47 years - - -
Number of subpopulations 1 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: The species has apparently always been rare, though the reasons for this are unclear and the range and population trends are difficult to judge because it is extremely elusive and occurs in highly inaccessible sheltered ravines. Based on data collected in 2011-2013, the population was estimated at 494 breeding individuals (95% CI 414-580) by linking occupancy surveys to habitat characteristics, territory density, and landscape attributes (Crampton et al. 2017), and there is no more recent estimate (L. Crampton in litt. 2023).

Trend justification: The population, whilst small, appears to be stable (Crampton et al. 2017). Since the 1960s the species' range has contracted, with the species no longer found at lower elevations (Scott et al. 1986). Few birds were detected after two hurricanes in the 1990s, but the population size is thought to have recovered to pre-hurricane numbers (Pratt 1994, Conant et al. 1998, Snetsinger et al. 1999). The most recent population estimate is 494 breeding individuals (95% CI 414-580) using data from 2011-2013, and previous estimates of 300-500 (using data from 1995–1998) and 270-525 birds (using data from 2003–2005) were extrapolated from surveys on a smaller proportion of streams within the range (Snetsinger et al. 1999, Woodworth et al. 2009, Crampton et al. 2017, USFWS 2018). Based on these data the population is assumed to have been stable since the mid-1990s (Crampton et al. 2017, USFWS 2018), though trends are difficult to determine given the lack of consistent methodologies (Fantle-Lepczyk et al. 2018). There is no more recent population estimate (L. Crampton in litt. 2023), with standard forest surveys being an unreliable sampling method for this species given its occurrence in highly inaccessible steep, narrow stream valleys (Crampton et al. 2017, Paxton et al. 2020). 
Population models have indicated a declining population under baseline conditions, though this contradicts assumptions that the population remains stable and may be due to inaccuracies in parameter estimation (Fantle-Lepczyk et al. 2018). Further study to refine mortality and reproductive estimates and to establish whether the population is stable or declining is urgently required, however even presumed to be stable the population remains highly restricted and susceptible to ongoing threats and stochastic events (Fantle-Lepczyk et al. 2018). Reintroduction of captive-bred individuals failed to lead to a significant population increase (Switzer et al. 2013); until declines in habitat quality are halted and predation by introduced mammals is addressed, the species will likely not recover. 


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
USA extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
USA Kauai Forests and Uplands

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Montane major resident
Altitude 1050 - 1300 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Climate change & severe weather Habitat shifting & alteration Timing Scope Severity Impact
Ongoing Whole (>90%) Negligible declines Medium Impact: 6
Stresses
Indirect ecosystem effects, Ecosystem degradation
Climate change & severe weather Storms & flooding Timing Scope Severity Impact
Past, Likely to Return Whole (>90%) Rapid Declines Past Impact
Stresses
Ecosystem degradation, Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Capra hircus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Ecosystem degradation
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Copsychus malabaricus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Competition
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Erigeron annuus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Ecosystem degradation
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Felis catus Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Garrulax canorus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Competition
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Hedychium gardnerianum Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Ecosystem degradation
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Horornis diphone Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Competition
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Plasmodium relictum Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Psidium cattleianum Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Pycnonotus cafer Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Competition
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Rattus rattus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Reduced reproductive success, Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Rubus argutus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Ecosystem degradation
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Sophonia rufofascia Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Competition
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Sphaeropteris cooperi Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Ecosystem degradation
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Sus domesticus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Ecosystem degradation
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Zosterops japonicus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Competition
Invasive and other problematic species, genes & diseases Problematic native species/diseases - Asio flammeus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Species mortality
Invasive and other problematic species, genes & diseases Viral/prion-induced diseases - Avipoxvirus Timing Scope Severity Impact
Ongoing Majority (50-90%) Negligible declines Low Impact: 5
Stresses
Species mortality

Recommended citation
BirdLife International (2024) Species factsheet: Puaiohi Myadestes palmeri. Downloaded from https://datazone.birdlife.org/species/factsheet/puaiohi-myadestes-palmeri 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.