Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
C2a(i) | C2a(i); D | C2a(i); D1 |
Year | Category | Criteria |
---|---|---|
2021 | Critically Endangered | C2a(i) |
2018 | Critically Endangered | C2a(i) |
2016 | Critically Endangered | C2a(i) |
2015 | Critically Endangered | C2a(i) |
2013 | Critically Endangered | C2a(i) |
2012 | Critically Endangered | C2a(i) |
2010 | Critically Endangered | C2a(i) |
2009 | Critically Endangered | C2a(i) |
2008 | Critically Endangered | |
2006 | 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 |
shelf island |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 41,100 km2 | medium |
Number of locations | 2-5 | - |
Severely fragmented? | yes | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 50-249 mature individuals | poor | estimated | 1999 |
Population trend | decreasing | poor | inferred | 2012-2029 |
Generation length | 5.4 years | - | - | - |
Number of subpopulations | 2-100 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The population is estimated to number 50-249 mature individuals, based on the assessment by BirdLife International (2001) that it "seems unlikely that there are more than a few hundred individuals... on each island [Panay and Negros], and there may only be a few tens". This estimate equates to 75-374 individuals in total, rounded here to 70-400 individuals.
Trend justification: During the 20th century, extensive forest loss occurred throughout the species range. On Negros, the species was fairly common in the 19th century but had become extremely rare by the 1930s (Baptista et al. 2020). However, recent deforestation analyses show that rates of forest loss are marginal at 2-4% (Tracewski et al. 2016; Global Forest Watch 2020) over three generations (16.2 years; Bird et al. 2020). Hence declines due to habitat loss are likely to have slowed, but the impact of hunting, including for the live bird trade, is likely to be driving declines substantially above this rate.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Philippines | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Philippines | Central Panay mountains |
Philippines | Cuernos de Negros |
Philippines | Mount Kanla-on Natural Park |
Philippines | North-west Panay peninsula (Pandan) |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Altitude | 300 - 1000 m | Occasional altitudinal limits | (max) 1200 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Agro-industry farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
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 | Problematic native species/diseases | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Unknown | Unknown | ||||||
|
|||||||||
Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Pets/display animals, horticulture | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Negros Bleeding-heart Gallicolumba keayi. Downloaded from
https://datazone.birdlife.org/species/factsheet/negros-bleeding-heart-gallicolumba-keayi 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.