Taxonomic note
Ceyx lepidus, C. margarethae, C. wallacii, C. cajeli, C. solitarius, C. dispar, C. mulcatus, C. sacerdotis, C. meeki, C. collectoris, C. nigromaxilla and C. gentianus (del Hoyo and Collar 2014) were previously lumped as C. lepidus following Sibley and Monroe (1990, 1993).
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 |
---|---|---|
- | - | D1 |
Year | Category | Criteria |
---|---|---|
2022 | Near Threatened | B1b(ii,iii); C2a(ii) |
2016 | Near Threatened | C2a(ii) |
2014 | Near Threatened | C2a(ii) |
2012 | Not Recognised | |
2008 | Not Recognised | |
2004 | Not Recognised | |
2000 | Not Recognised | |
1994 | Not Recognised | |
1988 | Not Recognised |
Migratory status | not a migrant | Forest dependency | medium |
Land-mass type | Average mass | 19 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 13,300 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 580-5800, 2500-5000 mature individuals | poor | inferred | 2020 |
Population trend | decreasing | - | suspected | 2016-2026 |
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 | 2.9 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: No species-specific population estimate has been generated for the species. Other Ceyx species have been recorded at densities of 2–10 birds/km2 (Bell 1982, Vernon 1985). In 2020, there was approximately 4,400 km2 of forest (excluding plantations) left in the species' range (Global Forest Watch 2022, based on data from Hansen et al. [2013] and methods disclosed therein). Assuming C. wallacii occurs at similar densities to other Ceyx and that approximately 10–20% of suitable habitat is occupied (a reflection of its apparently being quite common; F. Rheindt in litt. 2020), the population likely numbers 880–8,800, or 580–5,800 mature individuals. Given field observations, a best estimate of 2,500–5,000 mature individuals is suspected.
Trend justification: Forest loss in this species' range is equivalent to c.5–8% over ten years (Global Forest Watch 2022, based on data from Hansen et al. [2013] and methods disclosed therein). Because it requires some element of forested habitat to persist (i.e. it does not occur in agricultural areas and has not been recorded in plantations) but is at least partially tolerant of degradation, there is uncertainty in the extent to which a decline in forest cover reflects a decline in the population of this species. To account for these uncertainties, the population is suspected of having declined 1–9% over the past 10 years and, with no likely abatement in forest loss, this rate is projected into the future.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Indonesia | extant | native | yes |
Country/Territory | IBA Name |
---|
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Shrubland | Subtropical/Tropical Moist | suitable | resident |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | suitable | resident |
Altitude | 0 - 500 m | Occasional altitudinal limits | (max) 1300 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 | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Sula Dwarf-kingfisher Ceyx wallacii. Downloaded from
https://datazone.birdlife.org/species/factsheet/sula-dwarf-kingfisher-ceyx-wallacii on 22/12/2024.
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 22/12/2024.