Current view: Data table and detailed info
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: https://www.museum.lsu.edu/~Remsen/SACCBaseline.htm.
IUCN Red List criteria met and history
Red List criteria met
Red List history
Migratory status |
not a migrant |
Forest dependency |
medium |
Land-mass type |
continent
|
Average mass |
- |
Population justification: This species has an extremely small range, and it has been reported to be difficult to locate (Tobias et al. 1993, Tobias and Williams 1996), although it is considered locally abundant in suitable habitat (CEMAVE 2018). Reported densities are 156 pairs/km2 at Vale do Mambucaba and 89 pairs/km2 at ArirĂ³ (Gonzaga 2008), which collectively are thought to hold more than 90% of the total population (CEMAVE 2018). Although the population size has not been directly quantified, it is suspected to be smaller than 250 mature individuals, based on sightings by researchers within the range (CEMAVE 2018).
Based on an assumed minimum population density of 40 individuals/km2 (consistent with status as a locally common antwren), an upper density of 267 individuals/km2 (assumed equivalent to 89 pairs/km2), and assuming 11-45% of the mapped range is occupied, the population is here suspected to number 475-12,680 individuals . This equates to approximately 317-8,453 mature individuals, here rounded to 300-8,500 mature individuals. The population size is therefore placed in the band 50-8,500 mature individuals.
The number of subpopulations is not known. Based on discontinuities between areas with records, the species is assumed to have at least two subpopulations. According to the Brazilian national Red List, 90-100% of individuals are thought to comprise a single subpopulation (CEMAVE 2018). The largest subpopulation is therefore suspected to hold 45-8,500 mature individuals.
Trend justification: An ongoing slow population decline is suspected to be taking place, based on observational information (Tobias and Williams 1996) and remote-sensed data (Global Forest Watch 2020) on habitat loss. From 2010 to 2019, approximately 4% of tree cover was lost within the species's range (Global Forest Watch 2020). The species is tolerant of degraded habitat and occurs in scrubby habitats and secondary forest, so there is a low level of confidence in the population trend, but the species is suspected to be declining, with a suspected population reduction over the last ten years of 1-4%. In 2017, approximately 0.8% of forest within the species's range was lost within a single year (Global Forest Watch 2020). Extrapolating this rate over 10 years would equate to approximately 8%. Using this value as a maximum, the population is suspected to decline by 1-8% over the next decade.
Country/territory distribution
Important Bird and Biodiversity Areas (IBA)
Recommended citation
BirdLife International (2024) Species factsheet: Black-hooded Antwren Formicivora erythronotos. Downloaded from
https://datazone.birdlife.org/species/factsheet/black-hooded-antwren-formicivora-erythronotos 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.