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 |
---|---|---|
2024 | Near Threatened | C2a(i) |
2016 | Vulnerable | A2c+3c+4c;B1ab(i,ii,iii,iv,v);C2a(i) |
2012 | Vulnerable | A2c+3c+4c;B1ab(i,ii,iii,iv,v);C2a(i) |
2008 | Vulnerable | A2c; A3c; A4c; B1a+b(i,ii,iii,iv,v); C2a(i) |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Not Recognised |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 90,100 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 2500-9999 mature individuals | poor | estimated | 2023 |
Population trend | decreasing | poor | inferred | 2018-2028 |
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 | 2.88 years | - | - | - |
Number of subpopulations | 3-10 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The population size has not been quantified, but the species is described as scarce, apparently naturally occurring at low densities (Ridgely and Tudor 1994, Ridgely et al. 1998, J. Hornbuckle in litt. 1999; E. Horstmann in litt. 2000, 2007; see also eBird 2024). Using a density (based on occupancy of territorial pairs) of 0.8 mature individuals per km2 M. Sánchez Nivicela (in litt. 2024) derived an indicative population size of 3,641 mature individuals. The closely related Amazonian Royal Flycatcher O. coronatus was found to occur at a density of 0.5 pairs/km2 in Peru, equivalent to 1 mature individual/km2 (Sample et al. 2020). Acknowledging uncertainty in this value, the population size is placed in a band of 2,500-10,000 mature individuals.
Past, very rapid forest loss has resulted in considerable fragmentation of the remaining habitat, however there are at least two considerable portions of the range that are connected and while dispersal is not well-known it is suspected to be able to successfully disperse within a forested matrix. Accounting for the spatial distribution of the habitat modelled by M. Sánchez Nivicela (in litt. 2024) the largest subpopulation is likely to exceed one-third of the population size given, and therefore exceed 1,000 mature individuals (sRedList 2023).
Trend justification: This species' population is inferred to be declining, in line with habitat loss within its range and as a result of the fragmentation of remaining habitat patches (Ridgely and Greenfield 2001, eBird 2024). Up until the 1980s, deforestation in western Ecuador proceeded rapidly at a rate of 57% per decade (Dodson and Gentry 1991), so that now mostly small fragments remain (see Global Forest Watch 2023). Forest loss has however since slowed down; currently tree cover is lost at a rate of 2% over ten years (Global Forest Watch 2023, using Hansen et al. [2013] data and methods disclosed therein). There are no recent records from Juaneche Biological Research station, Bosque Protector Pedro Franco Dávila, where the species was regularly observed in the 1990s (Best and Kessler 1995, eBird 2024). While coverage at this site is lower in recent years, visits have taken place (e.g. Jansen and Jansen 2023) and it seems the species may have been lost from the site. Even considering the species' dependence on deciduous forests, and accounting for additional impacts of habitat degradation and fragmentation, population declines are likely slow. They are here tentatively placed in the band 1-9% over ten years.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Ecuador | extant | native | yes | |||
Peru | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Ecuador | Abras de Mantequilla |
Ecuador | Bosque Protector Cerro Blanco |
Ecuador | Bosque Protector Molleturo Mullopungo |
Ecuador | Bosque Protector Puyango |
Ecuador | Centro Científico Río Palenque |
Ecuador | Estación Científica Pedro Franco Dávila |
Ecuador | Hacienda Camarones |
Ecuador | Parque Nacional Machalilla y alrededores |
Ecuador | Reserva Biológica Tito Santos |
Ecuador | Reserva Buenaventura |
Ecuador | Reserva Ecológica Arenillas |
Ecuador | Reserva Ecológica Comunal Loma Alta |
Peru | Parque Nacional Cerros de Amotape |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Dry | major | resident |
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | suitable | resident |
Altitude | 0 - 970 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 | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | 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 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Pacific Royal Flycatcher Onychorhynchus occidentalis. Downloaded from
https://datazone.birdlife.org/species/factsheet/pacific-royal-flycatcher-onychorhynchus-occidentalis on 23/12/2024.
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 23/12/2024.