Taxonomic note
Anumara forbesi (del Hoyo and Collar 2016) was previously placed in the genus Curaeus following SACC (2005 & updates); 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: https://www.museum.lsu.edu/~Remsen/SACCBaseline.htm.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | C2a(i); D1 |
Year | Category | Criteria |
---|---|---|
2020 | Vulnerable | C2a(i); D1 |
2017 | Endangered | B2ab(i,ii,iii,iv,v) |
2016 | Endangered | B1ab(i,ii,iii,iv,v);C2a(i) |
2012 | Endangered | B1ab(i,ii,iii,iv,v);C2a(i) |
2008 | Endangered | B1a+b(i,ii,iii,iv,v); C2a(i) |
2004 | Endangered | |
2000 | Critically Endangered | |
1996 | Critically Endangered | |
1994 | Critically Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | medium |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 447,000 km2 | medium |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 600-10000 mature individuals | poor | estimated | 2018 |
Population trend | decreasing | poor | inferred | 2011-2024 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 1-10% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 1-10% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 1-10% | - | - | - |
Generation length | 4.33 years | - | - | - |
Number of subpopulations | 4-30 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The species appears to be naturally rare and has localised subpopulations. Based on the opinion of experts with experience of research within the species's range, the total population size is thought to be smaller than 10,000 mature individuals (de Melo Dantas and Albano 2018). Based on the maximum number of individuals seen at one locality (700), the population size is estimated to fall within the band 1,000-2,499 individuals (de Melo Dantas and Albano 2018, D. Lima in litt. 2020), which roughly equates to 667-1,667 mature individuals. The population size is therefore placed in the band 600-10,000 mature individuals.
The species is found in localised subpopulations separated from large areas of unsuitable habitat, and there are no records of individuals moving large distances between habitat patches (de Melo Dantas and Albano 2018). The species is therefore thought to have small subpopulations with fewer than 1,000 mature individuals in each subpopulation (de Melo Dantas and Albano 2018).
Trend justification: The area of forest with at least 30% canopy cover within the species's mapped range declined by 10% over a period of three generations (13 years) from 2006-2019 (Global Forest Watch 2020). The species is known to inhabit forest edges as well as sugar cane and mango plantations, and non-forest habitats, so it is not known whether the reduction in forest habitat has resulted in a similar reduction in population size, but the population size is tentatively inferred to be declining at a suspected rate of up to 10% over three generations (13 years).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Brazil | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Brazil | Mata do Estado (Mata do Sirigi) |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Grassland | Subtropical/Tropical Seasonally Wet/Flooded | major | resident |
Altitude | 0 - 890 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 | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Unknown | Unknown | ||||||
|
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Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Molothrus bonariensis | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Molothrus rufoaxillaris | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Unknown | Unknown | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Forbes's Blackbird Anumara forbesi. Downloaded from
https://datazone.birdlife.org/species/factsheet/forbess-blackbird-anumara-forbesi 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.