NT
Dark-rumped Swift Apus acuticauda



Taxonomy

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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - D1

Red List history
Year Category Criteria
2024 Near Threatened D1
2016 Vulnerable D1
2013 Vulnerable D1
2012 Vulnerable D1
2008 Vulnerable D1
2004 Vulnerable
2000 Vulnerable
1996 Vulnerable
1994 Vulnerable
1988 Threatened
Species attributes

Migratory status full migrant Forest dependency medium
Land-mass type continent
Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 290,000 km2 medium
Extent of Occurrence (non-breeding) 330,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 900-10000 mature individuals poor suspected 2024
Population trend stable - suspected -
Generation length 4.19 years - - -
Number of subpopulations 1 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: This species has been described as very local and scarce (Rasmussen and Anderton 2012). The number of individuals recorded in each eBird (2024) observation indicates that the population size is unlikely to be less than 250. However, it is possible that the population size could be fewer than 1,000 mature individuals. Given the significant lack of understanding surrounding the population, a precautionary estimate ranges from 900 to 10,000 individuals. This estimate considers both the apparent small population size and the substantial uncertainty, leaving room for the possibility of a larger population that has yet to be discovered.

Trend justification: The species has a broad range and there are no known threats that are thought to be causing significant global declines in the population. An analysis conducted via Global Forest Watch indicates a notable decline of 6.4% in forest cover spanning the period from 2010 to 2023 (3 generations) (Global Forest Watch (2024), based on data from Hansen et al. (2013) and methods therein). Primarily concentrated within the recognised resident range of the species, this reduction in forest cover could pose a concern for the species, however it is not thought to be heavily dependent on forest. The species has an expansive breeding range, with regions in Bhutan where the species is present, experiencing minimal forest cover loss. Furthermore, regions characterised by robust forest ecosystems, like Phawngpui National Park, are known for hosting healthy populations of A. acuticauda (Kasambe et al. 2014). The species also exhibits a high elevational tolerance, having been documented between 200 and 2,470 meters within India (Chantler and Kirwan 2020). Consequently, owing to potential accessibility constraints, suitable habitat extends beyond areas with higher rates of forest loss. Records at its known sites have remained stable for many years, for example at Cherrapunji (J. Eaton in litt. 2013), and it continues to be regularly reported at well-known sites (eBird 2024). Given the limited understanding of this species' ecology, assessing the extent to which forest cover loss poses a threat remains challenging, but it does not seem likely to have caused any significant population declines yet. Due to these factors the population is suspected to be stable in the absence of evidence for any declines or substantial threats.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Bhutan extant native yes
India extant native yes
Myanmar extant native yes yes
Thailand extant vagrant

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Bhutan Deothang / Narphang / Samdrup Jongkhar
Bhutan Tshangkha
India Blue Mountain (Phawngpui) National Park
India Cherapunjee: cliffs, gorges and sacred groves
India Dzuku Valley
India Khonoma Nature Conservation and Tragopan Sanctuary
India Lengteng Wildlife Sanctuary
India Murlen National Park
India Puliebadze-Dzukou-Zapfu
Thailand Doi Chiang Dao
Thailand Doi Inthanon
Thailand Mae Fang

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Lowland major non-breeding
Forest Subtropical/Tropical Moist Lowland major breeding
Forest Subtropical/Tropical Moist Montane suitable resident
Rocky areas (eg. inland cliffs, mountain peaks) major non-breeding
Rocky areas (eg. inland cliffs, mountain peaks) major breeding
Altitude 200 - 2470 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Biological resource use Logging & wood harvesting - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Unknown Unknown Unknown
Stresses
Ecosystem degradation

Recommended citation
BirdLife International (2024) Species factsheet: Dark-rumped Swift Apus acuticauda. Downloaded from https://datazone.birdlife.org/species/factsheet/dark-rumped-swift-apus-acuticauda on 23/11/2024.
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 23/11/2024.