Taxonomic note
Crithagra concolor (del Hoyo and Collar 2016) was previously placed in the genus Neospiza following Dowsett & Forbes-Watson (1993); 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 |
---|---|---|
C2a(ii) | C2a(i,ii); D | B1ab(iii,v)+2ab(iii,v); C2a(i,ii); D1 |
Year | Category | Criteria |
---|---|---|
2021 | Critically Endangered | C2a(ii) |
2018 | Critically Endangered | C2a(ii) |
2016 | Critically Endangered | B1ab(iii,v); C2a(ii) |
2015 | Critically Endangered | B1ab(iii,v);C2a(i,ii);D |
2013 | Critically Endangered | B1ab(iii,v);C2a(i,ii);D |
2012 | Critically Endangered | B1ab(iii,v);C2a(i,ii);D |
2009 | Critically Endangered | C2a(ii); D1 |
2008 | Critically Endangered | |
2004 | Critically Endangered | |
2000 | Critically Endangered | |
1996 | Critically Endangered | |
1994 | Critically Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 220 km2 | medium |
Area of Occupancy (breeding/resident) | 284 km2 | |
Number of locations | 6-10 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 50-249 mature individuals | poor | estimated | 2016 |
Population trend | decreasing | poor | inferred | - |
Generation length | 3.3 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The species is assumed to have a tiny population due to the scarcity of records. However, a recent extensive survey collated 39 records of this species, including many new localities, in altitude, and in secondary forest (de Lima et al. 2017). The species is very difficult to detect, so could be more abundant than current records suggest (Ward-Francis et al. 2015; de Lima et al. 2017), and whilst still likely to have a small population, the recent evidence suggests there could be >250 mature individuals. However, it is precautionarily placed in the range of 50-249 mature individuals.
Trend justification: The population is inferred to be declining as a result of ongoing habitat degradation, plus the impacts of introduced predators, however the rate of decline has not been estimated.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
São Tomé e Príncipe | extant | native | yes |
Country/Territory | IBA Name |
---|---|
São Tomé e Príncipe | Parque Natural Obô de São Tomé e Zona Tampão |
São Tomé e Príncipe | São Tomé lowland forests |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 100 - 1400 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Scale Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Rapid Declines | Past Impact | ||||||
|
|||||||||
Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Future | Minority (<50%) | Very Rapid Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Cercopithecus mona | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Civettictis civetta | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Mustela nivalis | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rattus rattus | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Unknown | Unknown | ||||||
|
|||||||||
Natural system modifications | Dams & water management/use - Large dams | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Rapid Declines | Low Impact: 5 | ||||||
|
|||||||||
Transportation & service corridors | Roads & railroads | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Sao Tome Grosbeak Crithagra concolor. Downloaded from
https://datazone.birdlife.org/species/factsheet/sao-tome-grosbeak-crithagra-concolor 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.