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 |
---|---|---|
- | B1ab(iii); D | B1ab(iii); D1+2 |
Year | Category | Criteria |
---|---|---|
2021 | Endangered | B1ab(iii); D |
2018 | Critically Endangered | C2a(ii) |
2016 | Critically Endangered | C2a(ii) |
2015 | Critically Endangered | C2a(ii) |
2013 | Critically Endangered | C2a(ii) |
2012 | Critically Endangered | C2a(ii) |
2010 | Critically Endangered | B1a+b(v); C2a(ii) |
2009 | Critically Endangered | B1a+b(v); C2a(ii) |
2008 | Critically Endangered | |
2004 | Critically Endangered | |
2000 | Critically Endangered | |
1996 | Critically Endangered | |
1994 | Critically Endangered | |
1988 | Not Recognised |
Migratory status | altitudinal migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 3,800 km2 | medium |
Area of Occupancy (breeding/resident) | 2,180 km2 | |
Number of locations | 2-5 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 230-300 mature individuals | good | estimated | 2021 |
Population trend | increasing | poor | observed | - |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 10-25% | - | - | - |
Generation length | 3.1 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: In 2019, the National Parrot Census counted 180-200 individuals at five sites across the Cordillera Central: 30 individuals in Murrillo (Tolima), 90-100 individuals in the Giles-Fuertes Nature Reserve in Cajamarca (Tolima), 10-20 individuals in the Loro Coroniazul Bird Reserve and El Mirador Municipality Reserve in Génova (Quindío), 20 individuals in Chaparral (Tolima) and 30 individuals at the Finca Cortaderal (Risaralda) (Fundación ProAves per P. Salaman in litt. 2019). The total population is currently estimated at 350-450 individuals (Fundación ProAves per A. Cortes in litt. 2021). This equates roughly to 230-300 mature individuals.
Trend justification: The species evidently declined in the past, but owing to coordinated conservation efforts at the species's stronghold the decline is historical and the species has been increasing since at least 2004 (Renjifo et al. 2014; P. Salaman in litt. 2019). It is assumed that habitat protection and the provision of artificial nestboxes quickly halted and reversed the decline, however the population increases only slowly and may be locally stable (P. Salaman in litt. 2019; E. Soler in litt. 2021).
At the time of the rediscovery in 2002, around 60 individuals were estimated (Rainforest Trust 2010). In 2010, the known population consisted of 164 individuals at two sites, and in 2019 the total population was estimated at 180-200 individuals (Fundación ProAves per P. Salaman in litt. 2019; A. Cortes in litt. 2021). Over the past ten years, the population thus increased by 10-25%.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Colombia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Colombia | Alto Quindío |
Colombia | Páramos y Bosques Altoandinos de Génova |
Colombia | Reserva Natural Ibanasca |
Colombia | Reserva Natural Semillas de Agua |
Colombia | Reservas Comunitarias de Roncesvalles |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Subtropical/Tropical Heavily Degraded Former Forest | marginal | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 2900 - 3150 m | Occasional altitudinal limits | 2600 - 3800 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Indigo-winged Parrot Hapalopsittaca fuertesi. Downloaded from
https://datazone.birdlife.org/species/factsheet/indigo-winged-parrot-hapalopsittaca-fuertesi 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.