Taxonomic note
Premnoplex tatei and P. pariae (del Hoyo and Collar 2016) were previously lumped as P. tatei following SACC (2005 & updates), Sibley and Monroe (1990, 1993) and 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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | B1ab(ii,iii) | B1ab(ii,iii)+2ab(ii,iii); D2 |
Year | Category | Criteria |
---|---|---|
2024 | Endangered | B1ab(ii,iii) |
2016 | Endangered | B1ab(i,ii,iii,v) |
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 | high |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 2,040 km2 | medium |
Area of Occupancy (breeding/resident) | 1,852 km2 | |
Number of locations | 2-5 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 5000-12800 mature individuals | medium | estimated | 1994 |
Population trend | decreasing | poor | suspected | 2017-2027 |
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) | 10-19% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 10-19% | - | - | - |
Generation length | 2.74 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The population size has not been quantified, but the species is described as uncommon or rare, and absent from seemingly suitable habitat (Hilty 2003, Greeney and Remsen Jr. 2020).
The closely related Premnoplex pariae, with which it was formerly considered conspecific, was found at a density of 0.8 individuals/ha (Evans et al. 1994). Assuming that P. tatei occurs at the same density, and further assuming that only around 10-20% of forests within the range are occupied to account for the species's rarity (per Hilty 2003), the population may number 7,520-19,200 individuals, roughly equating to 5,000-12,800 mature individuals. However, given the age of this estimate and the suspected slow decline of the population, an up-to-date estimate is required.
Trend justification: The species is suspected to be declining as a consequence of the loss, fragmentation and degradation of its forested habitat.
Over the past ten years, 4% of tree cover within the range has been lost; since 2017 this has been accelerating to a rate equivalent to 6% over ten years (Global Forest Watch 2023, using Hansen et al. [2013] data and methods disclosed therein). The species is strongly dependent on humid forests (Sharpe and Lentino 2015, Greeney and Remsen Jr. 2020) and therefore, population declines may exceed the rate of tree cover loss. Tentatively, the rate of population decline is therefore placed in the band 1-9% over the past ten years, accelerating to 10-19% since 2017.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Venezuela | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Venezuela | Parque Nacional El Guácharo |
Venezuela | Zona Protectora Macizo Montañoso del Turimiquire |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 800 - 2410 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Shifting agriculture | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
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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 | Wood & pulp plantations - Small-holder plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
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Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
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Recommended citation
BirdLife International (2024) Species factsheet: White-throated Barbtail Premnoplex tatei. Downloaded from
https://datazone.birdlife.org/species/factsheet/white-throated-barbtail-premnoplex-tatei on 24/11/2024.
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 24/11/2024.