Taxonomic note
Phoenicurus bicolor (del Hoyo and Collar 2016) was previously placed in the genus Rhyacornis following Sibley & Monroe (1990, 1993).
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 |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2020 | Near Threatened | C1+2a(i) |
2016 | Vulnerable | A2c+3c+4c;D2 |
2012 | Vulnerable | A2c+3c+4c;D2 |
2008 | Vulnerable | A2c; A3c; A4c; B1a+b(i,ii,iii,iv,v); D2 |
2006 | Vulnerable | |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Endangered | |
1994 | Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | does not normally occur in forest |
Land-mass type |
shelf island |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 95,300 km2 | medium |
Number of locations | 11-100 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 2500-9999 mature individuals | poor | suspected | 1999 |
Population trend | decreasing | poor | suspected | 2014-2024 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 10-20% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 10-20% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 10-20% | - | - | - |
Generation length | 2.8 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The population size has not been directly quantified. Density estimates range from one pair every 100-200 m (Kennedy et al. 2000) to one pair every 300 m on Mt. Polis. Assuming that the species is present through suitable habitat in the Cordillera Central as well as the Sierra Madre, the population size likely exceeds 2,500 mature individuals. Therefore, it is here placed in the band 2,500-9,999 mature individuals.
Trend justification: The population is believed to be undergoing a suspected decline of 10-20% over three generations (10 years; Bird et al. 2020) due to habitat loss and degradation affecting the upland streams required by the species. These forests appear to be highly sensitive to the impacts of logging, including siltation, and pollution from mining.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Philippines | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Philippines | Aurora Memorial National Park |
Philippines | Iglit - Baco Mountains |
Philippines | Mount Dingalan |
Philippines | Mount Pulag National Park |
Philippines | Northern Sierra Madre Natural Park |
Philippines | PeƱablanca Protected Landscape and Seascape |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Shrubland | Subtropical/Tropical Moist | suitable | resident |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | major | resident |
Altitude | 300 - 0 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
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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Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
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Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Rapid Declines | Medium Impact: 6 | ||||||
|
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Pollution | Agricultural & forestry effluents - Herbicides and pesticides | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Pollution | Agricultural & forestry effluents - Type Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Pollution | Industrial & military effluents - Seepage from mining | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Rapid Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Luzon Water-redstart Phoenicurus bicolor. Downloaded from
https://datazone.birdlife.org/species/factsheet/luzon-water-redstart-phoenicurus-bicolor on 22/11/2024.
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 22/11/2024.