Taxonomic note
Ceyx melanurus and C. mindanensis (del Hoyo and Collar 2014) were previously lumped as C. melanurus 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 |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2024 | Least Concern | |
2016 | Vulnerable | A2c+3c+4c |
2014 | Vulnerable | A2c+3c+4c |
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 | 23 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 166,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | decreasing | poor | suspected | 2019-2029 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 0-15% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 0-15% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 0-15% | - | - | - |
Generation length | 2.88 years | - | - | - |
Number of subpopulations | 2 | - | - | - |
Population justification: This species is poorly known. Described by Allen (2020) as local and uncommon, and the paucity of observations of this species in citizen science data (eBird 2024) would ostensibly suggest that it is a rare species. However, Ceyx are cryptic and have low detectability, with mist-netting often proving dwarf-kingfishers previously thought of as quite rare, to be quite common. This species' former conspecific, North Philippine Dwarf-kingfisher Ceyx melanurus, for example, similarly has fewer records in citizen science data, but was found to be common during mist-netting (e.g. Gomez et al. 2009). It seems likely therefore that Ceyx mindanensis is commoner than records suggest, especially given its tolerances of heavily degraded forest (see, e.g., de Leon et al. 2018). While its population size is therefore recorded as unknown, given the size of Mindanao (nearly 100,000 km2), the global population size is unlikely to be small.
Trend justification: The only plausible threat to this species is habitat loss and degradation. Although previously often regarded as dependent on virgin forest, it tolerates open forest and secondary growth, as do most Ceyx species (de Leon et al. 2018, Allen 2020). Global Forest Watch (2024, using data from Hansen et al. [2013] and methods disclosed therein) indicates that over the past 10 years, approximately 10-12% of forest canopy cover has been lost, but in many places this has been replaced with plantations which this species may inhabit, or may have overgrown. Accordingly, this value may not accurately reflect the population trend of this species, which is set to ongoing declines of 0-15% to account for considerable uncertainty.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Philippines | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Philippines | Basilan Natural Biotic Area |
Philippines | Bislig |
Philippines | Mount Agtuuganon and Mount Pasian |
Philippines | Mount Balatukan |
Philippines | Mount Dapiak-Mount Paraya |
Philippines | Mount Diwata Range |
Philippines | Mount Hamiguitan (Tumadgo peak) |
Philippines | Mount Hilong-hilong |
Philippines | Mount Kaluayan - Mount Kinabalian Complex |
Philippines | Mount Kampalili-Puting Bato |
Philippines | Mount Latian complex |
Philippines | Munai / Tambo |
Philippines | Pasonanca watershed |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Plantations | suitable | resident |
Artificial/Terrestrial | Subtropical/Tropical Heavily Degraded Former Forest | major | resident |
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 - 750 m | Occasional altitudinal limits | (max) 1000 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Shifting agriculture | 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 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: South Philippine Dwarf-Kingfisher Ceyx mindanensis. Downloaded from
https://datazone.birdlife.org/species/factsheet/south-philippine-dwarf-kingfisher-ceyx-mindanensis 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.