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.
SACC. 2005 and updates. A classification of the bird species of South America. Available at: https://www.museum.lsu.edu/~Remsen/SACCBaseline.htm.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | C2a(ii) |
Year | Category | Criteria |
---|---|---|
2021 | Vulnerable | C2a(ii) |
2016 | Vulnerable | C2a(i) |
2013 | Vulnerable | C2a(i) |
2012 | Vulnerable | C2a(i) |
2008 | Vulnerable | C2a(i) |
2006 | Vulnerable | |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Critically Endangered | |
1994 | Critically Endangered | |
1988 | Threatened |
Migratory status | unknown | Forest dependency | does not normally occur in forest |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 265,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1000-9999, 2500-9999 mature individuals | medium | estimated | 2014 |
Population trend | decreasing | poor | inferred | - |
Generation length | 1.99 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The species's population size is poorly known, but given that there were no documented records from 1959 to 1998, it is likely to be rare. It is fairly common at a handful of sites, with no known locality holding a population of more than c.35 individuals (Mazar Barnett et al. 1998, 2014, Imberti and Mazar Barnett 1999). Extensive surveys carried out between 1998 and 2006 at 58 wetlands distributed over an area of c.700,000 km2 detected a maximum of 175 individuals in total, at 22 localities that collectively held approximately 85 km2 of habitat (Mazar Barnett et al. 2014). Surveys in Santa Cruz in 2009-2013 detected at least one individual at each of two more localities (Roesler et al. 2014). Given the difficulty of detecting the species, there are likely to be undetected individuals. Nevertheless, the total population size is very unlikely to exceed 10,000 mature individuals, and could plausibly be less than 2,500 mature individuals (Mazar Barnett et al. 2014), so it is here placed in the band 1,000-9,999 mature individuals, with a best estimate in the range 2,500 - 9,999 mature individuals.
The subpopulation structure is poorly known, but a record of a vagrant individual in the Falkland Islands indicates that the species is able to disperse over large distances, so there is likely to be a degree of connectivity between habitat fragments. The population is therefore assumed to have a single subpopulation.
Trend justification: The species is threatened by continuing overgazing at some localities such as El Zurdo (A. de Miguel, I. Roesler and L. Fasola in litt. 2018), and by invasive American Mink Neovison vison, which is expanding its range (Mazar Barnett et al. 2014, Roesler et al. 2014, Fasola and Roesler 2016). Surveys in Santa Cruz found that the species's population density and site occupancy were negatively affected by the presence of mink (de Miguel et al. 2019). The species's range appears to have contracted considerably in the long-term, with no recent records from much of the known historical range. The species's population size is therefore inferred to be undergoing a continuing decline, the rate of which is unknown.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Argentina | extant | native | yes | |||
Chile | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Argentina | El Zurdo |
Argentina | La Angostura y Alto Río Chico |
Argentina | Laguna Nimez y costa aledaña del Lago Argentino |
Argentina | Parque Nacional Los Glaciares y adyacencias (Estancias El Sosiego, La Soledad y Anita) |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Grassland | Subtropical/Tropical Seasonally Wet/Flooded | major | resident |
Wetlands (inland) | Bogs, Marshes, Swamps, Fens, Peatlands | major | resident |
Wetlands (inland) | Freshwater Springs and Oases | suitable | resident |
Wetlands (inland) | Permanent Freshwater Lakes (over 8ha) | major | resident |
Wetlands (inland) | Permanent Freshwater Marshes/Pools (under 8ha) | major | resident |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | major | resident |
Altitude | 0 - 570 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 | ||||
Future | Minority (<50%) | Rapid Declines | Low Impact: 4 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Biological resource use | Gathering terrestrial plants - Unintentional effects (species is not the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Energy production & mining | Renewable energy | Timing | Scope | Severity | Impact | ||||
Future | Minority (<50%) | Very Rapid Declines | Low Impact: 5 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Neovison vison | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Natural system modifications | Dams & water management/use - Abstraction of ground water (agricultural use) | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
|||||||||
Natural system modifications | Dams & water management/use - Small dams | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Natural system modifications | Other ecosystem modifications | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Austral Rail Rallus antarcticus. Downloaded from
https://datazone.birdlife.org/species/factsheet/austral-rail-rallus-antarcticus 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.