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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | C2a(ii) | C2a(ii) |
Year | Category | Criteria |
---|---|---|
2020 | Endangered | C2a(ii) |
2016 | Endangered | C2a(i,ii) |
2013 | Endangered | C2a(i,ii) |
2012 | Vulnerable | B1ab(i,ii,iii,v);D1 |
2008 | Vulnerable | C2a(i); D1 |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 3,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 2000-12000 mature individuals | poor | estimated | 2020 |
Population trend | decreasing | medium | inferred | 2014-2024 |
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) | 1-9% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Generation length | 2 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The population size has not been quantified directly. Based on the recorded population densities of congeners (Selasphorus calliope and S. platycercus: 15-75 mature individuals/km2 [Santini et al. 2018]), and assuming that around 10% of the range is occupied to account for the rarity of the species (G. Angehr in litt. 2020), the population is estimated to fall within the band 2,235-11,175 mature individuals. To account for uncertainty in the estimate, the species is here placed in the band 2,000-12,000 mature individuals. Given that the species appears to be rare (G. Angehr in litt. 2020), it is conceivable that the true population size is closer to the lower end of the estimate.
Trend justification: The population trend has not been assessed directly. The species is threatened by habitat loss; however forests within the range are largely inaccessible and declines in tree cover are local and low (G. Angehr in litt. 2020, Global Forest Watch 2020). Given that the species is able to survive in degraded and secondary forests (G. Angehr in litt. 2013), forest loss is currently unlikely to drive rapid population declines. Local declines have however been observed in Veraguas (E. S. Jakub in litt. 2020). As the species is confined to a small range close to mountaintops, it is potentially vulnerable to climate change-related range shifts (G. Angehr in litt. 2020). Precautionarily, it is assumed that the species may be undergoing population declines in the future as suitable habitat is contracting at mountaintops. The rates of habitat loss and population declines have not been projected, but it is unlikely that they will exceed 10% over ten years.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Panama | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Panama | Cerro Santiago |
Panama | Santa Fé National Park |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | suitable | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Shrubland | Subtropical/Tropical High Altitude | suitable | resident |
Altitude | 1000 - 2520 m | Occasional altitudinal limits |
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 | ||||||
|
|||||||||
Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder 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 | ||||||
|
|||||||||
Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Whole (>90%) | Rapid Declines | Medium Impact: 6 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Pollution | Agricultural & forestry effluents - Herbicides and pesticides | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Glow-throated Hummingbird Selasphorus ardens. Downloaded from
https://datazone.birdlife.org/species/factsheet/glow-throated-hummingbird-selasphorus-ardens 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.