NT
Giant Conebill Conirostrum binghami



Taxonomy

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#.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - -

Red List history
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
Species attributes

Migratory status not a migrant Forest dependency high
Land-mass type Land-mass type - continent
Average mass -
Distribution

Estimate Data quality
Extent of Occurrence breeding/resident (km2) 1,380,000 medium
Severely fragmented? no -
Population and trend
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 distribution
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

Important Bird and Biodiversity Areas (IBA)
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

Habitats & altitude
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

Threats & impact
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
Stresses
Ecosystem degradation, Ecosystem conversion
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
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Wood & pulp plantations - Small-holder plantations Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
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
Stresses
Ecosystem degradation
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
Stresses
Ecosystem degradation, Ecosystem conversion

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.