Taxonomic note
Pogonotriccus lanyoni (del Hoyo and Collar 2016) was previously listed as Phylloscartes lanyoni.
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 |
---|---|---|
- | - | A3c+4c |
Year | Category | Criteria |
---|---|---|
2024 | Vulnerable | A3c+4c |
2016 | Endangered | B1ab(i,ii,iii,v);C2a(i) |
2012 | Endangered | B1ab(i,ii,iii,v);C2a(i) |
2008 | Endangered | B1a+b(i,ii,iii,v); C2a(i) |
2004 | Endangered | |
2000 | Endangered | |
1996 | Endangered | |
1994 | Endangered | |
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) | 24,900 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1000-2499 mature individuals | poor | suspected | 2016 |
Population trend | decreasing | poor | suspected | 2017-2027 |
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) | 30-49% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Generation length | 2.41 years | - | - | - |
Number of subpopulations | 6-100 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: There are no estimates of the population size (Renjifo et al. 2016). Nevertheless, based on the localised distribution and low number of records, it is suspected that the population numbers less than 2,500 mature individuals. It is here tentatively placed in the band 1,000-2,499 mature individuals, though an accurate quantification is urgently required.
Trend justification: The population trend has not been investigated, but declines are suspected on the basis of habitat loss.
The rate of tree cover loss within the range has been fairly low over the past ten years (6-9%; Renjifo et al. 2016, Global Forest Watch 2023, using Hansen et al. [2013] data and methods disclosed therein). Logging activities appear to be small-scale, but widespread across the entire range (Global Forest Watch 2023), and it has been hypothesised that the overall rate of habitat loss exceeds the rate of tree cover loss substantially due to the additive impacts of forest degradation (Renjifo et al. 2016). Tentatively, the rate of population decline over the past ten years is here placed in the band 20-29% (per Renjifo et al. 2016).
Rates of habitat loss appear to have started accelerating in c.2017 (Global Forest Watch 2023). It is projected that as a consequence of deforestation, the species will lose an additional 60% of its habitat between 2015 and 2040 (Negret et al. 2021). Assuming an exponential rate of decline, this equates to a rate of habitat loss of 46% over the next ten years. Further assuming that population declines are roughly equivalent to the rate of habitat loss, they are here placed in the band 30-49% over the next ten years.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Colombia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Colombia | Embalse de San Lorenzo y Jaguas |
Colombia | Refugio Río Claro |
Colombia | Reserva Regional Bajo Cauca Nechí |
Colombia | Serranía de las Quinchas |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Subtropical/Tropical Heavily Degraded Former Forest | suitable | resident |
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Forest | Subtropical/Tropical Moist Montane | suitable | resident |
Altitude | 450 - 1960 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 | ||||||
|
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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 | ||||||
|
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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 | ||||||
|
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Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
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Recommended citation
BirdLife International (2024) Species factsheet: Antioquia Bristle-tyrant Pogonotriccus lanyoni. Downloaded from
https://datazone.birdlife.org/species/factsheet/antioquia-bristle-tyrant-pogonotriccus-lanyoni 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.