Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions 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 |
---|---|---|
- | - | C2a(i) |
Year | Category | Criteria |
---|---|---|
2021 | Vulnerable | C2a(i) |
2016 | Endangered | B1ab(ii,iii,iv,v);C2a(i) |
2012 | Endangered | B1ab(ii,iii,iv,v);C2a(i) |
2008 | Endangered | B1a+b(ii,iii,iv,v); C2a(i) |
2004 | Endangered | |
2000 | Endangered | |
1996 | Critically Endangered | |
1994 | Critically Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 102,000 km2 | medium |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 2500-9999 mature individuals | poor | estimated | 2021 |
Population trend | decreasing | poor | inferred | 2020-2030 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 4-14% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 5-17% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 5-17% | - | - | - |
Generation length | 2.42 years | - | - | - |
Number of subpopulations | 4-100 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The species is locally common (CEMAVE 2018), but there are few recent records from Espírito Santo or Minas Gerais (2018). Based on the minimum and median recorded densities of the congener Glaucis hirsutus (2 and 3.3 individuals per km2, respectively), the area of tree cover with at least 50% canopy cover within the species's range in 2010 (28,600 km2; Global Forest Watch 2021), and assuming that between 5 and 25% of the tree cover is occupied by the species (based on the species having a localised distribution), the population size is suspected to fall within the range of 2,800 - 24,000 individuals, roughly equating to 1,900 - 16,000 mature individuals. The species appears to require well-preserved forest (Silveria 2008), of which little remains in southern Bahia (B. Phalan in litt. 2021). Furthermore, G. hirsutus is a much commoner species than G. dohrnii, so the population density of the latter species may be expected to be lower. The true population size may therefore be expected to fall towards the lower end of the band, and is estimated to be smaller than 10,000 mature individuals.
The species's remaining habitat is fragmented and there are no records of individuals moving between sites, so there are assumed to be multiple subpopulations, with fewer than 1,000 individuals in the largest subpopulation (CEMAVE 2018).
Trend justification:
Local extinctions have occurred, including at localities formerly thought to be strongholds of the species, such as the Córrego Grande Biological Reserve (Hinkelmann 1999). Remote sensing data on tree cover loss within the species's range indicates that approximately 9% of tree cover with at least 50% canopy cover was lost over ten years from 2009-2019 (Global Forest Watch 2021). Extrapolating forward, it is estimated that up to 12% may be lost over the next decade, assuming that the rate of forest loss remains constant. The species is generally found in primary forest and so its population is inferred to be undergoing an ongoing continuing decline as a result of this habitat loss, at a rate of 4-14% over the past ten years, and 5-17% over the next ten years.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Brazil | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Brazil | Alto Cariri |
Brazil | Boa Nova / Serra da Ouricana |
Brazil | Estação Veracruz |
Brazil | Parque Nacional do Pau Brasil / Trancoso |
Brazil | Serra Bonita |
Brazil | Serra de Itamaraju |
Brazil | Serras das Lontras e do Javi |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Altitude | 0 - 500 m | Occasional altitudinal limits | (max) 600 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 | 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 | Whole (>90%) | Slow, Significant Declines | Medium Impact: 7 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
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 | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | 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 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Trend Unknown/Unrecorded | 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 | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Transportation & service corridors | Roads & railroads | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Hook-billed Hermit Glaucis dohrnii. Downloaded from
https://datazone.birdlife.org/species/factsheet/hook-billed-hermit-glaucis-dohrnii on 22/11/2024.
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 22/11/2024.