Data Zone
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 |
|---|---|---|
| - | - | C2a(i) |
| Year | Category | Criteria |
|---|---|---|
| 2021 | Vulnerable | C2a(i) |
| 2016 | Vulnerable | B1ab(i,ii,iii,iv,v) |
| 2012 | Vulnerable | B1ab(i,ii,iii,iv,v) |
| 2008 | Vulnerable | B1a+b(i,ii,iii,iv,v) |
| 2004 | Vulnerable | |
| 2000 | Vulnerable | |
| 1994 | Lower Risk/Near Threatened | |
| 1988 | Near Threatened |
| Migratory status | not a migrant | Forest dependency | medium |
| Land-mass type | Average mass | - |
| Estimate | Data quality | |
|---|---|---|
| Extent of Occurrence (breeding/resident) | 35,200 km2 | medium |
| Severely fragmented? | no | - |
| Estimate | Data quality | Derivation | Year of estimate | |
|---|---|---|---|---|
| Population size | 2000-3000 mature individuals | poor | estimated | 2021 |
| Population trend | decreasing | poor | inferred | 2017-2027 |
| Rate of change over the past 10 years/3 generations (longer of the two periods) | 1-19% | - | - | - |
| Rate of change over the future 10 years/3 generations (longer of the two periods) | 1-19% | - | - | - |
| Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 1-19% | - | - | - |
| Generation length | 2.39 years | - | - | - |
| Number of subpopulations | 3-4 | - | - | - |
Population justification:
This species is described as locally common (Turner and de Juana, 2020). Based on this, taking the lowest of seven estimates for congeners, including Lesser Striped-swallow Hirundo abyssinica and Rufous-chested Swallow Hirundo semirufa of 2 individuals/km2 (Vernon 1985), and assuming it inhabits 20% of the forest within its range (9,380 km2 [Global Forest Watch 2021]), the population is may be 3,752 individuals. This is roughly equivalent to 2,500 mature individuals. The population is therefore estimated to fall in the band 2,000-3,000 mature individuals.
Trend justification: Population trends have shown evidence of decline over the past few decades, owing to habitat loss and degradation from shifting agriculture and predation by invasive mammals (Dod 1992, Keith et al. 2003, Townsend 2006). No data are available to estimate recent population trends, however, this species is suspected to be declining in line with ongoing habitat loss and degradation. Data from Global Forest Watch (2021) showed that forest cover throughout the species's range declined by 4.7% over the last three generations (10 years). Based on forest loss data between 2017-2020 (Global Forest Watch 2021), and projected forward over three generations, the species habitat is likely to decline by <2%. With the additional threat of invasive predators, the species is suspected to be declining at a rate of between 1-19% over three generations.
| Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
|---|---|---|---|---|---|---|
| Dominican Republic | extant | native | yes | |||
| Haiti | extant | native | yes | |||
| Jamaica | possibly extinct | native | yes |
| Country/Territory | IBA Name |
|---|---|
| Dominican Republic | Armando Bermudez National Park |
| Dominican Republic | Eastern Bahoruco |
| Dominican Republic | Ebano Verde Scientific Reserve |
| Dominican Republic | Nalga de Maco-Río Limpio |
| Dominican Republic | Parque Nacional Dr Juan Bautista Pérez Rancier (Valle Nuevo) |
| Dominican Republic | Sierra de Bahoruco National Park |
| Dominican Republic | Sierra de Neyba |
| Haiti | Aux Becs-Croisés |
| Haiti | Aux Cornichons |
| Haiti | Aux Diablotins |
| Haiti | Bois Musicien |
| Jamaica | Blue Mountains |
| Jamaica | Cockpit Country |
| Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
|---|---|---|---|
| Artificial/Terrestrial | Arable Land | suitable | resident |
| Artificial/Terrestrial | Pastureland | suitable | resident |
| Artificial/Terrestrial | Urban Areas | suitable | resident |
| Forest | Subtropical/Tropical Dry | suitable | resident |
| Forest | Subtropical/Tropical Moist Lowland | suitable | resident |
| Forest | Subtropical/Tropical Moist Montane | major | resident |
| Grassland | Subtropical/Tropical Dry | suitable | resident |
| Altitude | 800 - 2000 m | Occasional altitudinal limits | (min) 0 m |
| 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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| Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rattus rattus | Timing | Scope | Severity | Impact | ||||
| Past, Likely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
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| Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Sturnus vulgaris | Timing | Scope | Severity | Impact | ||||
| Unknown | Unknown | Unknown | Unknown | ||||||
|
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Recommended citation
BirdLife International (2024) Species factsheet: Golden Swallow Tachycineta euchrysea. Downloaded from
https://datazone.birdlife.org/species/factsheet/golden-swallow-tachycineta-euchrysea 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.