Taxonomic note
Myiothlypis basilica (del Hoyo and Collar 2016) was previously placed in the genus Basileuterus and listed as B. basilicus 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 |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2021 | Near Threatened | D1 |
2016 | Vulnerable | B1ab(i,ii,iii) |
2012 | Vulnerable | B1ab(i,ii,iii) |
2008 | Vulnerable | B1a+b(i,ii,iii) |
2006 | Vulnerable | |
2004 | Vulnerable | |
2000 | Lower Risk/Near Threatened | |
1994 | Lower Risk/Near Threatened | |
1988 | Lower Risk/Least Concern |
Migratory status | not a migrant | Forest dependency | low |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 1,898 km2 | medium |
Area of Occupancy (breeding/resident) | 1,072 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1000-3000 mature individuals | poor | suspected | 2021 |
Population trend | stable | poor | suspected | 1998-2008 |
Generation length | 2.55 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The population size has not been quantified directly. To account for its apparent rarity, it has been suggested to occur at a density of 5-10 individuals/km2 derived on density estimates of congeners (M. nigrocristata and Basileuterus melanogenys; Renjifo et al. 2016), though the species may be rarer than this (E. Botero-Delgadillo in litt. 2021). Based on an area of habitat of 462 km2, the population is suspected to number up to 2,300-4,600 individuals (Renjifo et al. 2016). This roughly equates to up to 1,500-3,000 mature individuals and to account for its rarity the population is here placed in the band 1,000-3,000 mature individuals.
The subpopulation structure has not been assessed, but based on its tolerance of converted habitats it is tentatively assumed that all individuals belong to the same subpopulation.
Trend justification: Tree cover loss has been negligible within the range (<1% over the past ten years; Global Forest Watch 2020). Moreover, the species is also found in second growth and appears to tolerate habitat loss and degradation (Renjifo et al. 2016; Curson 2020). Tentatively the population is assessed as stable.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Colombia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Colombia | Cuchilla de San Lorenzo |
Colombia | Valle del Río Frío |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | suitable | resident |
Shrubland | Subtropical/Tropical High Altitude | major | resident |
Altitude | 2300 - 3000 m | Occasional altitudinal limits | (min) 2100 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%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Scale Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
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Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
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Natural system modifications | Fire & fire suppression - Trend Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
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Recommended citation
BirdLife International (2024) Species factsheet: Santa Marta Warbler Myiothlypis basilica. Downloaded from
https://datazone.birdlife.org/species/factsheet/santa-marta-warbler-myiothlypis-basilica 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.