Taxonomic source(s)
AERC TAC. 2003. AERC TAC Checklist of bird taxa occurring in Western Palearctic region, 15th Draft. Available at: http://www.aerc.eu/DOCS/Bird_taxa_of_the_WP15.xls.
Brooke, M. de L. 2004. Albatrosses and Petrels Across the World. Oxford University Press, Oxford.
Christidis, L. and Boles, W.E. 2008. Systematics and Taxonomy of Australian Birds. CSIRO Publishing, Collingwood, Australia.
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.
Robertson, C. J. R.; Nunn, G. B. 1998. Towards a new taxonomy for albatrosses. In: Robertson, G.; Gales, R. (ed.), Albatross biology and conservation, pp. 13-19. Surrey Beatty & Sons, Chipping Norton, Australia.
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 |
---|---|---|
- | A4bd; B2ab(v) | A4bd; B2ab(v) |
Year | Category | Criteria |
---|---|---|
2018 | Endangered | A4bd; B2ab(v) |
2016 | Endangered | A4bd; B2ab(v) |
2012 | Endangered | A4bd;B2ab(v) |
2010 | Endangered | A4b,d; B2a+b(v) |
2008 | Endangered | A4b,d; B2a+b(v) |
2007 | Endangered | |
2005 | Endangered | |
2004 | Endangered | |
2003 | Endangered | |
2000 | Lower Risk/Near Threatened | |
1994 | Not Recognised | |
1988 | Not Recognised |
Migratory status | full migrant | Forest dependency | does not normally occur in forest |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 29,100,000 km2 | medium |
Extent of Occurrence (non-breeding) | 16,800,000 km2 | medium |
Area of Occupancy (breeding/resident) | 80 km2 | medium |
Number of locations | 4 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 35000-73500 mature individuals | poor | estimated | 2012 |
Population trend | decreasing | medium | estimated | 1983-2055 |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 50-79% | - | - | - |
Generation length | 23.7 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification:
On Gough Island, the population was estimated at c.5,300 breeding pairs in 2000-2001 (Cuthbert and Sommer 2004). In 2015, the number of breeding pairs in the Tristan da Cunha group was estimated to be 15,250 on Tristan da Cunha Island, 4000 on Nightingale Island in 2007, 40 on Middle Island in 2010, 210 on Stoltenhoff Island in 2009 (Fraser et al. 1988, Ryan and Ronconi 2011, RSPB unpubl. data) equating to 52,000 mature individuals (range: 35,000-73,500).
Trend justification: On Inaccessible Island, a partial count in 1999-2000 suggests that the population may have decreased since the late 1980s (Ryan and Moloney 2000). On Nightingale, the population has declined from 3,000 pairs in 1972-1974 to 1,000 pairs in 1999 (P. G. Ryan in litt. 2000), and counts at 4 sites indicate an annual decrease of 3-4% between 2005-2015 (RSPB, Tristan Government unpublished data). Counts of the Gough Island study colony indicate that numbers within this small area underwent a period of decline (from 1982 to 1994) followed by an increase (1994 to 2008), with numbers now at similar levels to the early 1980s. Population counts from 11 representative areas of Gough Island (c. 5% of breeding habitat) indicate a decline of 2-3% per year, similar to population modelling with 20 years of demographic data (1982-2001) predicts annual rates of decrease of between 1.5-2.8% on Gough Island and 5.5% on Tristan da Cunha (Cuthbert et al. 2003; though one small study area is stable, perhaps because of immigration), and overall declines are estimated to exceed 70% over 72 years (three generations), placed here in the band 50-79% because of the level of uncertainty involved.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Angola | extant | native | yes | |||
Argentina | extant | native | yes | |||
Australia | extant | vagrant | ||||
Brazil | extant | native | yes | |||
Falkland Islands (Malvinas) | extant | vagrant | ||||
High Seas | extant | native | yes | |||
Mozambique | extant | native | yes | |||
Namibia | extant | native | yes | |||
New Zealand | extant | vagrant | yes | |||
South Africa | extant | native | yes | |||
St Helena (to UK) | extant | native | yes | |||
Uruguay | extant | native | yes | |||
USA | extant | vagrant |
Country/Territory | IBA Name |
---|---|
Brazil | Trindade e Martim Vaz |
St Helena (to UK) | Gough Island |
St Helena (to UK) | Inaccessible Island |
St Helena (to UK) | Nightingale Island group |
St Helena (to UK) | Tristan Island |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Grassland | Tundra | major | breeding |
Marine Coastal/Supratidal | Sea Cliffs and Rocky Offshore Islands | major | breeding |
Marine Neritic | Pelagic | major | non-breeding |
Marine Neritic | Pelagic | major | breeding |
Marine Oceanic | Epipelagic (0-200m) | major | non-breeding |
Marine Oceanic | Epipelagic (0-200m) | major | breeding |
Altitude | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Biological resource use | Fishing & harvesting aquatic resources - Unintentional effects: (large scale) [harvest] | 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 | ||||
Past, Unlikely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Mus musculus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Sus scrofa | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Atlantic Yellow-nosed Albatross Thalassarche chlororhynchos. Downloaded from
https://datazone.birdlife.org/species/factsheet/atlantic-yellow-nosed-albatross-thalassarche-chlororhynchos on 26/12/2024.
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 26/12/2024.