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.
SACC. 2005 and updates. A classification of the bird species of South America. Available at: https://www.museum.lsu.edu/~Remsen/SACCBaseline.htm.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2024 | Least Concern | |
2016 | Vulnerable | A2c+3c+4c;B1ab(i,ii,iii,iv,v) |
2012 | Vulnerable | A2c+3c+4c;B1ab(i,ii,iii,iv,v) |
2008 | Vulnerable | A2c; A3c; A4c; B1a+b(i,ii,iii,iv,v) |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 41,700 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 12000-20000 mature individuals | poor | suspected | 2023 |
Population trend | decreasing | poor | inferred | 2017-2027 |
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 | 3.08 years | - | - | - |
Number of subpopulations | 2-10 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The population size has not been quantified. Density has not been reported, but the congener S. ucayalae has been recorded at between 4.7 and 7.7 individuals per square kilometer in south-east Peru (Lloyd 2004). Based on the distribution of records and noting that the species is uncommon, if only 20% of the modelled area of suitable habitat (12,786 km2 [M. Sanchez-Nivicela in litt. 2024]) is occupied, the population can be inferred to be between 12,000 and 19,700 mature individuals. This is in line with the assessment of the species' status in Ecuador, which judged the population to fall between 2,500-9,999 mature individuals (see Freile et al. 2019). Ecuador holds roughly 20% of the mapped global distribution, hence a crude scaling of this gives a suspected number of 12,500-49,999 mature individuals. Tentatively the species population is suspected to fall between 12,000-20,000 mature individuals.
Trend justification: This species is declining; while in the past it was described as fairly common to common, it is now considered uncommon and local (Jiggins et al. 1999, Schulenberg et al. 2007, Freile and Restall 2018). The Ecuadorian assessment also recognised that there was a continuing decline in mature individuals (Freile et al. 2019).
Declines are thought to be caused by habitat destruction. Within the range, 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). This value however does not account for the additional impacts of forest degradation and fragmentation. Considering this, rates of population declines are possibly higher than the rate of tree cover loss alone suggests. Tentatively, population declines are here placed in the band 1-9% over ten years, noting that the trend rate may vary locally.
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 | Alamor-Celica |
Ecuador | Bosque Protector Jatumpamba-Jorupe |
Ecuador | Cañón del río Catamayo |
Ecuador | Catacocha |
Ecuador | Cazaderos-Mangaurquillo |
Ecuador | La Tagua |
Ecuador | Reserva Comunal Bosque de Angashcola |
Ecuador | Tambo Negro |
Ecuador | Utuana-Bosque de Hanne |
Peru | Alto Valle del Saña |
Peru | Bosque de Cuyas |
Peru | Chiñama |
Peru | Laquipampa |
Peru | Parque Nacional Cerros de Amotape |
Peru | Suyo-La Tina |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Subtropical/Tropical Heavily Degraded Former Forest | suitable | resident |
Forest | Subtropical/Tropical Dry | major | resident |
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 400 - 2900 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 | ||||||
|
|||||||||
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 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Rufous-necked Foliage-gleaner Syndactyla ruficollis. Downloaded from
https://datazone.birdlife.org/species/factsheet/rufous-necked-foliage-gleaner-syndactyla-ruficollis 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.