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) | C2a(i); D | C2a(i); D1 |
Year | Category | Criteria |
---|---|---|
2019 | Critically Endangered | C2a(i) |
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 | Endangered | |
1996 | Endangered | |
1994 | Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 51,800 km2 | medium |
Number of locations | 11-100 | - |
Severely fragmented? | yes | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 50-249 mature individuals | poor | suspected | 2018 |
Population trend | decreasing | poor | inferred | 2006-2020 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Generation length | 4.6 years | - | - | - |
Number of subpopulations | 2-10 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The species is considered to be rare (CEMAVE 2018). According to the National Red List of Brazil, it is possible to estimate, with a high confidence level, that the total population does not exceed 250 mature individuals and that each subpopulation has fewer than 50 mature individuals (CEMAVE 2018). The population size is therefore placed in the band 50-249 mature individuals.
Trend justification: The species was previously easily observed in Espírito Santo, but there have been few, if any, records from the state since the 1990s, despite a large number of observers and researchers searching for the species in the region, and it may now be extirpated from the state (CEMAVE 2018, A. Lees in litt. 2019, G. Kirwan in litt. 2019, eBird 2019). From this information, it is inferred that the population size has declined recently. Based on records of the species, the species's extent of occurrence is inferred to have declined by approximately 30-40% since the 1990s; based on this, a population reduction of 20-29% over three generations is suspected (13.8 years). An analysis of remote-sensed data on forest loss estimated that forest was lost within the species's range from 2000-2012 at a rate equivalent to 4% across three generations (Tracewski et. al. 2016).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Brazil | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Brazil | Alto Cariri |
Brazil | Bandeira / Macarani |
Brazil | Estação Veracruz |
Brazil | Serra Bonita |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Altitude | 0 - 270 m | Occasional altitudinal limits |
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 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
|||||||||
Residential & commercial development | Commercial & industrial areas | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Other household goods | subsistence, national |
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Banded Cotinga Cotinga maculata. Downloaded from
https://datazone.birdlife.org/species/factsheet/banded-cotinga-cotinga-maculata on 05/12/2024.
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 05/12/2024.