Taxonomic note
Pseudosaltator rufiventris (del Hoyo and Collar 2016) was previously placed in the genus Saltator following SACC (2005 & updates); Sibley and 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 |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2020 | Least Concern | |
2018 | Near Threatened | C2a(i) |
2016 | Near Threatened | C2a(i) |
2012 | Near Threatened | C2a(i) |
2008 | Near Threatened | C2a(i) |
2004 | Near Threatened | |
2000 | Lower Risk/Near Threatened | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Lower Risk/Least Concern |
Migratory status | not a migrant | Forest dependency | medium |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 247,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 10000-19999 mature individuals | poor | estimated | 2020 |
Population trend | decreasing | poor | suspected | 2014-2024 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Generation length | 3.4 years | - | - | - |
Number of subpopulations | 2-10 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The species is in general uncommon, but can be locally common (Stotz et al. 1996, Pearman 1997, S. Mayer in litt. 1999), and is potentially more widespread than known to date. The population in Bolivia is thought to exceed 10,000 individuals (S. Mayer in litt. 1999), which roughly equates to more than 6,500 mature individuals. Therefore, the global population is here tentatively placed in the band 10,000-19,999 mature individuals.
Trend justification: The population trend has not been estimated directly. The species is threatened by habitat loss, and it is suspected that the conversion of native scrub and woodland for agricultural use, together with an increase in wildfires, are causing a slow population decline. Forests loss within the range has been negligible over the past three generations (<1% over 10.2 years; Global Forest Watch 2020). It is therefore tentatively assumed that the combined impacts of the loss of forests and the loss of scrubland through logging and fires are causing a population decline of <10% over three generations.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Argentina | extant | native | yes | |||
Bolivia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Argentina | Alto Calilegua |
Argentina | Caspala y Santa Ana |
Argentina | Cerro Negro de San Antonio |
Argentina | Cuesta del Obispo |
Argentina | Fincas Santiago y San Andrés |
Argentina | Santa Victoria, Cañani y Cayotal |
Bolivia | Azurduy |
Bolivia | Cerro Q'ueñwa Sandora |
Bolivia | Quebrada Mojón |
Bolivia | Reserva Biológica Cordillera de Sama |
Bolivia | Reserva Nacional de Flora y Fauna Tariquía |
Bolivia | Southern slopes of Tunari National Park (Vertiente Sur del Parque Nacional Tunari IBA) |
Bolivia | Yungas Superiores de Apolobamba |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Arable Land | marginal | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Shrubland | Subtropical/Tropical High Altitude | major | resident |
Altitude | 2500 - 4000 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 | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Small-holder plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Rufous-bellied Mountain-tanager Pseudosaltator rufiventris. Downloaded from
https://datazone.birdlife.org/species/factsheet/rufous-bellied-mountain-tanager-pseudosaltator-rufiventris 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.