Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.
SACC. 2005 and updates. A classification of the bird species of South America. Available at: https://www.museum.lsu.edu/~Remsen/SACCBaseline.htm.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2020 | Vulnerable | D1 |
2016 | Endangered | D |
2013 | Endangered | D |
2012 | Endangered | D |
2010 | Endangered | D1 |
2009 | Critically Endangered | B1a+b(i,ii,iii,v) |
2008 | Critically Endangered | |
2004 | Critically Endangered | |
2000 | Critically Endangered | |
1996 | Critically Endangered | |
1994 | Critically Endangered | |
1988 | Threatened |
Migratory status | nomadic | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 44,300 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1000 mature individuals | good | observed | 2019 |
Population trend | increasing | good | observed | 2000-2010 |
Generation length | 4.9 years | - | - | - |
Number of subpopulations | 3 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: From the initial 81 individuals that were rediscovered in 1999, the species increased to 2,600 individuals in 2019, which include at least 1,000 mature individuals (Salaman et al. 2019).
Trend justification: Once abundant across its range, habitat loss and subsequent lack of nest site availability as well as hunting led to it almost becoming extinct by the end of the 20th century (Salaman et al. 2019). The species has not been recorded in Ecuador since the 1990s, and only in 1997 a small flock was rediscovered in Colombia (Krabbe and Sornoza 1996, Salaman et al. 1999a). Since then, intense conservation efforts caused an exceptional recovery and increase in population size. From an initial 81 individuals in 1999, the species increased to 1,100 individuals in 2010, to 1,400 individuals in 2013 and to 2,600 individuals in 2019 (Fundación ProAves in litt. 2010, Salaman et al. 2019). Despite the overall positive trend, local declines are observed in the population at Cubarral, which decreased from 70 individuals counted in 2009 to less than ten individuals counted in 2020 (Fundación ProAves in litt. 2020).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Colombia | extant | native | yes | |||
Ecuador | possibly extinct | native | yes |
Country/Territory | IBA Name |
---|---|
Colombia | Bosques Montanos del Sur de Antioquia |
Colombia | Cafetales de Támesis |
Colombia | Cuenca del Río Toche |
Colombia | Reservas Comunitarias de Roncesvalles |
Colombia | Sumapaz Natural National Park |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 1200 - 3400 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 | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | No decline | Low Impact: 5 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | No decline | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Minority (<50%) | Rapid Declines | Past Impact | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Rapid Declines | Past Impact | ||||||
|
|||||||||
Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Yellow-eared Parrot Ognorhynchus icterotis. Downloaded from
https://datazone.birdlife.org/species/factsheet/yellow-eared-parrot-ognorhynchus-icterotis on 21/12/2024.
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 21/12/2024.