Taxonomic note
Amazona farinosa and A. guatemalae (del Hoyo and Collar 2014) were previously lumped as A. farinosa following Sibley and Monroe (1990, 1993).
Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2022 | Least Concern | |
2016 | Near Threatened | A4cd |
2014 | Near Threatened | A4cd |
2012 | Not Recognised | |
2008 | Not Recognised | |
2004 | Not Recognised | |
2000 | Not Recognised | |
1994 | Not Recognised | |
1988 | Not Recognised |
Migratory status | not a migrant | Forest dependency | low |
Land-mass type | Average mass | 626 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 12,200,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | poor | - | - |
Population trend | decreasing | - | suspected | 2000-2029 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 10-19% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 10-19% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 10-19% | - | - | - |
Generation length | 9.56 years | - | - | - |
Number of subpopulations | 2-100 | - | - | - |
Population justification: The population size has not been quantified. The species can be locally common in parts of its range, both in primary and mature secondary forest (Collar et al. 2020, O. Ottema in litt. 2020). The geographically disjunct population in the Brazilian Atlantic Forest was found to be genetically distinct from that in the greater Amazon Basin (Hellmich et al. 2021); therefore the species forms at least two separate subpopulations.
Trend justification: The population is undergoing a decline caused by habitat loss and the impacts of hunting and trapping (Collar et al. 2020). Since 2000, tree cover within the range has been lost at a rate equivalent to roughly 13% over three generations (Global Forest Watch 2021, using Hansen et al. [2013] data and methods disclosed therein). Rates of deforestation vary between the range; forest loss is historically more severe in the Atlantic Forest of Brazil (Fernandes et al. 2019, Global Forest Watch 2021, using Hansen et al. [2013] data and methods disclosed therein), while forests in parts of the Amazon Basin and Guinanan Shield remain largely pristine (O. Ottema in litt. 2020, Global Forest Watch 2021, using Hansen et al. [2013] data and methods disclosed therein). The species appears to tolerate some habitat degradation, but it is susceptible to hunting and trapping (Collar et al. 2020, D. F. Cisneros-Heredia in litt. 2022). Based on this evidence, population declines are placed in the band 10-19% over three generations (28.8 years).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Bolivia | extant | native | yes | |||
Brazil | extant | native | yes | |||
Colombia | extant | native | yes | |||
Ecuador | extant | native | yes | |||
French Guiana | extant | native | yes | |||
Guyana | extant | native | yes | |||
Panama | extant | native | yes | |||
Peru | extant | native | yes | |||
Suriname | extant | native | yes | |||
Venezuela | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Colombia | Bojonawi |
Colombia | Estrella Fluvial Inírida |
Colombia | Riberas de la Cuenca Baja del Río Inírida |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Subtropical/Tropical Heavily Degraded Former Forest | marginal | resident |
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Forest | Subtropical/Tropical Moist Montane | suitable | resident |
Altitude | 0 - 1100 m | Occasional altitudinal limits | (max) 1600 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Agro-industry farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Transportation & service corridors | Roads & railroads | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Pets/display animals, horticulture | national, international |
Recommended citation
BirdLife International (2024) Species factsheet: Southern Mealy Amazon Amazona farinosa. Downloaded from
https://datazone.birdlife.org/species/factsheet/southern-mealy-amazon-amazona-farinosa on 23/12/2024.
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 23/12/2024.