Taxonomic note
Fringilla teydea and F. polatzeki (del Hoyo and Collar 2016) were previously lumped as F. teydea following AERC TAC (2003); Cramp et al. (1977-1994); Sibley and 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 |
---|---|---|
- | D | D1+2 |
Year | Category | Criteria |
---|---|---|
2021 | Endangered | D |
2016 | Endangered | D |
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 | 30 g |
Estimate | Data quality | |
---|---|---|
Number of locations | 2 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 430 mature individuals | good | estimated | 2019 |
Population trend | increasing | poor | observed | - |
Generation length | 3.24 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The population size is estimated to be 430 individuals, with 362 at Inagua (36 km2) and 68 at La Cumbre (21 km2) (Carrascal et al., 2019), estimated from breeding surveys, suggesting a total population of 645 individuals. These form part of the same subpopulation, as colour-marked birds from Inagua were first found breeding at La Cumbre, before captive-reared birds were released there to reinforce the wild population. Population density estimates vary: apart from the two years following the 2007 forest fire, densities in Inagua have remained stable, around 10 birds / km² (Moreno et al., 2018), with the highest recorded density of 17.7 chaffinches / km² in 2019 (Carrascal et al., 2019). In La Cumbre, estimates have increased from 1.12 in 2016 to 3.3 chaffinches / km² in 2019 (Carrascal et al., 2019).
Trend justification: The results of the annual monitoring scheme show clearly that the species population is currently increasing, and can best be described as having fluctuated within a fairly narrow range over most of the last twenty years (Carrascal et al. 2016). Although the devastating fire in 2007 caused the population to halve in 2008, it subsequently recovered rapidly at an average annual rate of 24% (Moreno et al., 2018) with numbers back up to pre-fire levels by 2011, around 50% higher again by 2016, and continuing to increase as shown by the 2015-2020 annual surveys (Carrascal et al., 2019).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Spain | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Spain | Pajonales, Ojeda, Inagua and La Data pine woodlands |
Spain | Tamadaba pine woodland |
Spain | Tauro pine woodland |
Spain | Tirajana pine woodland |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Temperate | major | resident |
Altitude | 700 - 1800 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Rapid Declines | Past Impact | ||||||
|
|||||||||
Human intrusions & disturbance | Recreational activities | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Problematic native species/diseases - Dendrocopos major | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Problematic native species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Very Rapid Declines | Medium Impact: 7 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Gran Canaria Blue Chaffinch Fringilla polatzeki. Downloaded from
https://datazone.birdlife.org/species/factsheet/gran-canaria-blue-chaffinch-fringilla-polatzeki on 24/11/2024.
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 24/11/2024.