Taxonomic note
Conirostrum binghami (del Hoyo and Collar 2016) was previously placed in the genus Oreomanes and listed as O. fraseri following AOU (1998 & supplements); Sibley & Monroe (1990, 1993); Stotz et al. (1996).
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.
SACC. 2005 and updates. A classification of the bird species of South America. Available at: #http://www.museum.lsu.edu/~Remsen/SACCBaseline.htm#.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2021 | Near Threatened | A2c+3c+4c |
2016 | Near Threatened | A2c+3c+4c |
2012 | Near Threatened | A2c+3c+4c |
2008 | Near Threatened | A2c; A3c; A4c |
2004 | Near Threatened | |
2000 | Lower Risk/Near Threatened | |
1994 | Lower Risk/Near Threatened | |
1988 | Near Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
Land-mass type - continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence breeding/resident (km2) | 1,380,000 | medium |
Severely fragmented? | no | - |
Value | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Number of mature individuals | unknown | not applicable | not applicable | 0 |
Population trend | decreasing | poor | suspected | 2015-2025 |
Decline % (10 years/3 generations future) | 20-29 | - | - | - |
Decline % (10 years/3 generations past and future) | 20-29 | - | - | - |
Number of subpopulations | 5 | - | - | - |
Percentage in largest subpopulation | 1-89 | - | - | - |
Generation length (years) | 3.1 | - | - | - |
Population justification: The global population size has not been quantified, but the species is described as uncommon and patchily distributed (Mason and Burns 2020). Due to its disjunct range, it is tentatively assessed as forming at least five subpopulations.
Trend justification: Data on precise population trends are lacking, but this rare and habitat-restricted species is suspected to be in moderate decline owing to the ongoing destruction of Polylepis woodlands throughout its range (Cahill and Matthysen 2007; Mason and Burns 2020).
Country/Territory | Presence | Origin | Resident | Breeding | Non-breeding | Passage |
---|---|---|---|---|---|---|
Argentina | extant | native | yes | |||
Bolivia | extant | native | yes | |||
Chile | extant | native | yes | |||
Colombia | extant | native | yes | |||
Ecuador | extant | native | yes | |||
Peru | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Bolivia | Yungas Superiores de Apolobamba |
Bolivia | Bosque de Polylepis de Madidi |
Bolivia | Parque Nacional Sajama |
Bolivia | Reserva Biológica Cordillera de Sama |
Bolivia | Southern slopes of Tunari National Park (Vertiente Sur del Parque Nacional Tunari IBA) |
Ecuador | El Ángel - Cerro Golondrinas and surrounding areas |
Ecuador | Mindo and western foothills of Volcan Pichincha |
Ecuador | Cajas-Mazán |
Ecuador | Refugio de Vida Silvestre Pasochoa |
Ecuador | Reserva Ecológica Antisana (west) and adjacent areas |
Ecuador | Parque Nacional Cayambe-Coca |
Ecuador | Yanuncay-Yanasacha |
Peru | Cerro Huanzalá-Huallanca |
Peru | Champará |
Peru | Chiguata |
Peru | Parque Nacional Huascarán |
Peru | Reserva Nacional Pampa Galeras |
Bolivia | Bosque de Polylepis de Sanja Pampa |
Bolivia | Bosque de Polylepis de Mina Elba |
Argentina | Santa Victoria, Cañani y Cayotal |
Peru | Cotahuasi |
Peru | Cordillera Huayhuash y Nor-Oyón |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 3200 - 4500 m | Occasional altitudinal limits | 2700 - 4850 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Small-holder plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
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Recommended citation
BirdLife International (2023) Species factsheet: Conirostrum binghami. Downloaded from
http://datazone.birdlife.org/species/factsheet/giant-conebill-conirostrum-binghami on 29/09/2023.
Recommended citation for factsheets for more than one species: BirdLife International (2023) IUCN Red List for birds. Downloaded from
http://datazone.birdlife.org on 29/09/2023.