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.
Fjeldså, J. 1983. A Black Rail from Junín, central Peru: Laterallus jamaicensis tuerosi ssp. n. (Aves: Rallidae). Steenstrupia: 277-282.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | A2ace+3ce+4ace | A2ace+3ce+4ace |
Year | Category | Criteria |
---|---|---|
2021 | Endangered | A2ace+3ce+4ace |
2019 | Endangered | A2ace+3ce+4ace |
2016 | Near Threatened | A2c+3c+4c |
2012 | Near Threatened | A2c+3c+4c |
2008 | Near Threatened | A2c; A3c; A4c |
2006 | Near Threatened | |
2004 | Near Threatened | |
2000 | Lower Risk/Near Threatened | |
1994 | Lower Risk/Least Concern | |
1988 | Near Threatened |
Migratory status | full migrant | Forest dependency | does not normally occur in forest |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 40,400,000 km2 | medium |
Extent of Occurrence (non-breeding) | 39,700,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 10000-49999 mature individuals | poor | suspected | 2019 |
Population trend | decreasing | poor | estimated | 2018-2028 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 50-79% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 50-79% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 50-79% | - | - | - |
Generation length | 2.9 years | - | - | - |
Population justification: The global population size of this species has not been quantified directly and a distinct paucity of data renders the calculation of reliable estimates difficult. The subspecies jamaicensis, which occurs in eastern North and Central America as well as in the Caribbean, was estimated in the year 2000 to number 25,000-100,000 individuals, roughly equating to 15,000-70,000 mature individuals (Wetlands International 2020). However, given the dramatic declines witnessed in this subspecies in the years since, it would appear that this figure is a considerable overestimate. Watts (2016) recently provided an accurate estimate for the population of jamaicensis residing on the USA's eastern coast between New England and Florida, 455-1,315 breeding pairs or 910-2,630 mature individuals, however this population does not incorporate those individuals that comprise the Texan, central USA, Caribbean or Brazilian individuals of the same subspecies. No other population estimates are thought to be currently available for jamaicensis. The subspecies coturniculus, which occurs in California and northern Mexico, is estimated at 10,000-25,000 individuals, roughly equating to 7,000-17,000 mature individuals (Wetlands International 2020). There are no estimates available for the subspecies murivagans and salinasi in western South America (Wetlands International 2020). As a result, the global population is tentatively placed in the band 10,000-49,999 mature individuals however, such estimates require confirmation and are liable to change should more accurate estimates be provided.
Trend justification: This species is facing a number of serious threats which are thought to be causing declines in many parts of its range. The number of recent records suggest it is extremely scarce or no longer occurs in a number of former areas.
A recent projection of the future resilience of the subspecies jamaicensis in the eastern U.S.A. based on survey data of known populations used different scenarios of sea level rise, land management and the combined effects of both; it shows that the species is undergoing a steep decline and that there is a high probability that the species will be extirpated in the area by 2068 (USFWS 2018a). The surveys give evidence of a population decline at 90% along the east coast of the country since the early 1990s (USFWS 2018b), which is projected to continue. This decline equates to a rate of c. 60-69% over a ten year period and it is precautionarily assumed that subspecies jamaicensis is declining at this rate throughout its entire range.
The other three subspecies coturniculus, murivagans, and salinasi inhabit similar habitats and are likely faced with the same threats posed to jamaicensis, particularly those associated with climate change, and are therefore assumed to be undergoing declines at a similar rate. The rate of population decline for the global population is therefore tentatively placed in the band 50-79% across a ten year period, although further detailed population assessments are required to confirm this trend.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Antigua and Barbuda | extant | vagrant | ||||
Argentina | extant | native | yes | |||
Bahamas | extant | vagrant | ||||
Belize | extant | native | yes | |||
Bermuda (to UK) | extant | vagrant | yes | |||
Brazil | extant | native | yes | |||
Chile | extant | native | yes | |||
Colombia | extant | uncertain | yes | |||
Costa Rica | extant | native | yes | |||
Cuba | extant | native | yes | |||
Dominican Republic | extant | native | yes | |||
Guatemala | extinct | native | yes | |||
Haiti | extant | native | yes | |||
Honduras | extant | native | yes | |||
Jamaica | extant | native | yes | |||
Mexico | extant | native | yes | |||
Panama | extant | native | yes | |||
Peru | extant | native | yes | |||
Puerto Rico (to USA) | extant | native | yes | |||
USA | extant | native | yes | yes | yes | |
Virgin Islands (to USA) | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Chile | Humedal de Batuco |
Cuba | Ciénaga de Zapata |
Honduras | Mocorón |
Peru | Río Tambo y Lagunas de Mejía |
USA | Bear Island Wildlife Management Area |
USA | Bill Williams River National Wildlife Refuge |
USA | Imperial National Wildlife Refuge |
USA | Imperial Reservoir |
USA | Lower Colorado River Valley |
USA | Mittry Lake State Wildlife Area |
USA | San Pablo Bay Wetlands |
USA | Southern Dorchester County |
USA | St. Johns National Wildlife Refuge |
USA | Suisun Marsh |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Marine Intertidal | Salt Marshes (Emergent Grasses) | major | breeding |
Wetlands (inland) | Bogs, Marshes, Swamps, Fens, Peatlands | major | breeding |
Altitude | 0 - 4100 m | Occasional altitudinal limits |
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 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Climate change & severe weather | Droughts | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
|||||||||
Climate change & severe weather | Storms & flooding | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
|||||||||
Natural system modifications | Dams & water management/use - Abstraction of ground water (unknown use) | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Pollution | Agricultural & forestry effluents - Type Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Pollution | Industrial & military effluents - Type Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Black Rail Laterallus jamaicensis. Downloaded from
https://datazone.birdlife.org/species/factsheet/black-rail-laterallus-jamaicensis on 23/11/2024.
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 23/11/2024.