Taxonomic note
Recent mtDNA study suggests that present species is closest to C. canorus, the two being a sister-clade to C. gularis and C. rochii (Payne 2005). In 2014 Cuculus saturatus (del Hoyo and Collar 2014) incorporated C. optatus following the suggestion they were vocally indistinguishable, however the previous treatment, with both separated as species, is here reinstated after Xia et al. (2016) demonstrated that they are vocally distinct.
An earlier concept (recognised prior to 2006) treated C. saturatus (with optatus/horsfieldi: see note under C. optatus) as conspecific with C. lepidus (Sibley and Monroe 1990, 1993). Monotypic.
Taxonomic source(s)
Handbook of the Birds of the World and BirdLife International. 2021. Handbook of the Birds of the World and BirdLife International digital checklist of the birds of the world. Version 6. Available at: https://datazone.birdlife.org/userfiles/file/Species/Taxonomy/HBW-BirdLife_Checklist_v6_Dec21.zip.
Payne, R. B. 2005. The cuckoos. Oxford University Press, Oxford, U.K.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2021 | Least Concern | |
2016 | Not Recognised | |
2014 | Not Recognised | |
2013 | Least Concern | |
2012 | Least Concern | |
2009 | Least Concern | |
2008 | Least Concern | |
2007 | Least Concern | |
2004 | Not Recognised | |
2000 | Not Recognised | |
1994 | Not Recognised | |
1988 | Not Recognised |
Migratory status | full migrant | Forest dependency | medium |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 7,610,000 km2 | |
Extent of Occurrence (non-breeding) | 10,300,000 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | decreasing | - | inferred | 2011-2022 |
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 | 3.71 years | - | - | - |
Population justification: The global population size has not been quantified, but is thought to be large as the species is described as 'common and widespread' in at least parts of its range (Payne 2005).
Trend justification: Remote sensing data on tree cover loss indicate that approximately 13% of tree cover with at least 50% canopy cover was lost from the species's non-breeding range, and approximately 5% from the breeding range, over the past three generations (11 years; Global Forest Watch 2021). These figures may underestimate the true rate of forest loss, especially in the non-breeding range, as the tree cover data may include plantations. However, the species has has been recorded in some types of plantation and in gardens during the non-breeding season (Payne and Kirwan 2020). The species's population size is therefore suspected to be declining at a rate of less than 20% over three generations.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Bangladesh | extant | native | yes | yes | ||
Bhutan | extant | native | yes | |||
Cambodia | extant | native | yes | |||
China (mainland) | extant | native | yes | yes | ||
India | extant | native | yes | |||
Indonesia | extant | native | yes | yes | ||
Laos | extant | native | yes | yes | ||
Malaysia | extant | native | yes | yes | ||
Myanmar | extant | native | yes | yes | ||
Nepal | extant | native | yes | |||
Pakistan | extant | native | yes | |||
Philippines | extant | native | yes | |||
Thailand | extant | native | yes | yes | ||
Vietnam | extant | native | yes | yes |
Country/Territory | IBA Name |
---|
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Plantations | suitable | breeding |
Artificial/Terrestrial | Plantations | suitable | non-breeding |
Forest | Subtropical/Tropical Moist Lowland | suitable | breeding |
Forest | Subtropical/Tropical Moist Lowland | suitable | non-breeding |
Forest | Subtropical/Tropical Moist Montane | major | breeding |
Forest | Temperate | major | breeding |
Altitude | 0 - 4500 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 | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Pets/display animals, horticulture | subsistence, national, international |
Recommended citation
BirdLife International (2024) Species factsheet: Himalayan Cuckoo Cuculus saturatus. Downloaded from
https://datazone.birdlife.org/species/factsheet/himalayan-cuckoo-cuculus-saturatus on 04/12/2024.
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 04/12/2024.