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(ii) | B1ab(i,ii,iii,v)+2ab(i,ii,iii,v); C2a(i,ii); D | B1ab(i,ii,iii,v)+2ab(i,ii,iii,v); C2a(i,ii); D1+2 |
Year | Category | Criteria |
---|---|---|
2021 | Critically Endangered | C2a(ii) |
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 | |
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) | 31 km2 | medium |
Area of Occupancy (breeding/resident) | 28 km2 | |
Number of locations | 2-5 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 136-182 mature individuals | good | estimated | 2013 |
Population trend | decreasing | medium | inferred | - |
Generation length | 4.71 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The global population is estimated at 136-182 mature individuals (Rivera-Milán et al. 2015).
The population structure has not been assessed. While the species's two strongholds around Mt Hartman National Park and on the Perseverance and adjacent Woodford estates are separated by 9 km of highly converted habitat (Rusk 2017), there are occasional records of single individuals dispersing outside of these areas (Rivera-Milán et al. 2015, Rusk 2017). It is therefore tentatively assumed that the individuals in both areas are able to get in contact, forming just one subpopulation, though this requires confirmation.
Trend justification: The population was estimated at 98-124 mature individuals in 1998, climbing to 182 mature individuals by 2003-2004. Although these figures suggest that the population may have increased between 1998 and 2004, the latter estimate included c. 30 mature individuals discovered in 2003, and increases may reflect an improvement in sampling methods. However, the population declined after category IV hurricane Ivan caused severe damage in 2004, and the three years after the hurricane the population was still 25% below the numbers from 2004, with a maximum of 136 mature individuals (Rusk 2017). In 2013, the population was estimated at 136-182 mature individuals (Rivera-Milán et al. 2015).
While the population appears to have stabilised or even increased over the past three generations (14.1 years; Bird et al. 2020), it shows fluctuations in relation to hurricanes (Baptista et al. 2020). The intensity, and probably the frequency, of hurricanes in the Atlantic are projected to increase with climate change (see e.g., Knutson et al. 2010; Walsh et al. 2016). Therefore, it is inferred that the population is continuing to decline, as the population is deemed unable to recover between events of major reductions caused by hurricanes, in conjunction with other threats.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Grenada | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Grenada | Beausejour / Grenville Vale |
Grenada | Mount Hartman |
Grenada | Perseverance |
Grenada | Woodford |
Grenada | Woodlands of Grenada |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Dry | major | resident |
Altitude | 0 - 150 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 | ||||
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 | ||||||
|
|||||||||
Climate change & severe weather | Droughts | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Rapid Declines | High Impact: 8 | ||||||
|
|||||||||
Climate change & severe weather | Storms & flooding | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Very Rapid Declines | High Impact: 9 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Didelphis marsupialis | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Herpestes auropunctatus | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Named species | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Slow, Significant Declines | Medium Impact: 7 | ||||||
|
|||||||||
Pollution | Air-borne pollutants - Type Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Residential & commercial development | Tourism & recreation areas | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Very Rapid Declines | Medium Impact: 6 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Grenada Dove Leptotila wellsi. Downloaded from
https://datazone.birdlife.org/species/factsheet/grenada-dove-leptotila-wellsi 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.