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 |
---|---|---|
- | - | B1ab(ii,iii,iv) |
Year | Category | Criteria |
---|---|---|
2022 | Vulnerable | B1ab(ii,iii,iv) |
2016 | Vulnerable | A2c+3c+4c;B1ab(i,ii,iii,v) |
2012 | Vulnerable | A2c+3c+4c;B1ab(i,ii,iii,v) |
2008 | Vulnerable | A2c; A3c; A4c; B1a+b(i,ii,iii,v) |
2005 | 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 | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 5,650 km2 | medium |
Area of Occupancy (breeding/resident) | 3,000 km2 | |
Number of locations | 6-10 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 19000 mature individuals | poor | inferred | 2016 |
Population trend | decreasing | poor | suspected | 2015-2027 |
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) | 20-29% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Generation length | 4.16 years | - | - | - |
Number of subpopulations | 2-100 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The population size or density have not been quantified directly, but the species is described as common (Greeney 2020). Based on observed densities of congeners (G. rufocinerea: 80 individuals/km2; G. milleri: 102 individuals/km2; G. urraoensis: 94 individuals/km2; Renjifo et al. 2016 and references therein) and precautionarily assuming that this species occurs at the lowest density and that one-third of suitable habitat is occupied, the population is inferred to number 28,600 individuals (Renjifo et al. 2016). This roughly equates to 19,000 mature individuals.
Trend justification: The species is suspected to decline based on ongoing habitat loss within the range (Renjifo et al. 2016). Over the past three generations (12.5 years; Bird et al. 2020), tree cover loss has been low at <2% (Global Forest Watch 2022, using Hansen et al. [2013] data and methods disclosed therein). Despite occasionally venturing into cleared, open spaces and edge habitat the species strictly depends on humid montane forests (Greeney 2020) and as such it is suspected that population declines may exceed the rate of habitat loss. The rate of past decline is here placed in the band 1-9% over three generations.
Since around 2016, tree cover loss has been accelerating (Global Forest Watch 2022), and projections of habitat loss to deforestation suggest that between 2015 and 2040 the species will lose 21% of suitable habitat (Negret et al. 2021). This equates to a rate of habitat loss of 18% over three generations. Precautionarily assuming that population declines exceed this rate by about half to account for additional impacts of forest degradation, the population may decline by 20-29% over three generations from 2015 onwards.
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 de San Salvador |
Colombia | Valle del Río Frío |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 1390 - 2730 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 | ||||||
|
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Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Santa Marta Antpitta Grallaria bangsi. Downloaded from
https://datazone.birdlife.org/species/factsheet/santa-marta-antpitta-grallaria-bangsi 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.