Taxonomic note
Thalassarche melanophris (del Hoyo and Collar 2014) was previously listed as T. melanophrys.
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 |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2018 | Least Concern | |
2017 | Least Concern | |
2016 | Near Threatened | A4bd |
2013 | Near Threatened | A4bd |
2012 | Endangered | A4bd |
2010 | Endangered | A4b,d |
2008 | Endangered | A4b,d |
2005 | Endangered | |
2004 | Endangered | |
2003 | Endangered | |
2002 | Vulnerable | |
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 |
shelf island |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 177,000,000 km2 | medium |
Area of Occupancy (breeding/resident) | 24,100 km2 | |
Number of locations | 10 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1400000 mature individuals | good | estimated | 2015 |
Population trend | increasing | medium | estimated | 1979-2043 |
Generation length | 21.5 years | - | - | - |
Population justification: The Falklands Islands (Islas Malvinas) holds the largest number of breeding individuals, estimated at 475,500-535,000 pairs in 2010; Wolfaardt 2012). Most other breeding sites holding large numbers of breeding individuals are in Chile with 55,000 pairs estimated on Diego Ramirez in 2003, 58,000 pairs on Ildefonso in 2012 (Robertson et al. 2013), and 15,500 pairs on Diego de Almagro in 2002 (Lawton et al. 2003). The population size on South Georgia (Georgias del Sur) is difficult to estimate, but based on Poncet et al. (2006) and assuming the rate of decline was c.4% (similar to that of Bird Island), the population there may have been down to 56,000 pairs by 2012 (ACAP unpubl. data). However, this may be an underestimate as, based on surveys conducted in 2014/15 covering 30% of the South Georgia (Georgias del Sur) population, declines actually could have been at c.1.8% per year between 2005 and 2014 (Poncet et al. 2006, A. Wolfaardt in litt. 2016). There are an estimated c.5,800 pairs in other populations (Antipodes, Campbell, Heard and MacDonald, Crozet, Kerguelen, Macquarie, Snares; ACAP unpubl. data), giving a potential global population of c.700,000 pairs, which equates to 1,400,000 mature individuals.
Trend justification: Surveys of the Falkland Islands (Islas Malvinas) population have suggested this population is on the increase, with a 2010 archipelago-wide survey revealing (through aerial and ground-based surveying) an annual increase of at least 4% between 2005 and 2010. This is supported by further aerial surveys from later in the 2010 breeding season and demographic data (Wolfaardt 2012). From this it has also been concluded that the population of Black-browed Albatross on these islands has likely increased since the first archipelago-wide survey in 2000, and potentially since the first ground-based surveys on Beauchêne and Steeple Jason islands in the 1980s. Chilean populations are also likely increasing, as work suggests that the Diego Ramirez and Ildefonso archipelagos (supporting c.85% of the Chilean population) increased by 52% and 18% respectively between 2002 and 2011 (or 23% for both sites combined) (Robertson et al. 2013). Further surveys in 2014 indicated that the Diego Ramirez population increased by a further 29% between 2011 and 2014, while the numbers at Ildefonso remained stable (A. Wolfaardt in litt. 2016). The trend for South Georgia (Georgias del Sur) appears to be a decline, previously estimated as 4% per year, but now better estimated, based on surveys conducted in 2014/15 covering 30% of the South Georgia (Georgias del Sur) population, at c.1.9% per year between 2003/4 and 2014/5 (Poncet et al. 2006, A. Wolfaardt in litt. 2016, Poncet et al. 2017).
With the Falklands Islands (Islas Malvinas) and Chilean populations making up the vast majority of the global population it is highly likely that this is currently increasing, and potentially has been since the 1980s. The generation length for this species is long (21.5 years), and data is not available to fully assess population trends over 3 generations into the past. However, given the newer information regarding trends in Chile and South Georgia (Georgias del Sur) it now seems unlikely that the species is in the process of undergoing a decline over 3 generations (commencing in 1980 and continuing into the future).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Angola | extant | native | yes | |||
Antarctica | extant | native | yes | |||
Argentina | extant | native | yes | |||
Australia | extant | native | yes | |||
Bouvet Island (to Norway) | extant | uncertain | ||||
Brazil | extant | native | yes | |||
Chile | extant | native | yes | |||
Denmark | extant | vagrant | ||||
Ecuador | extant | uncertain | ||||
Falkland Islands (Malvinas) | extant | native | yes | |||
Fiji | extant | vagrant | yes | |||
French Polynesia | extant | uncertain | ||||
French Southern Territories | extant | native | yes | |||
Heard Island and McDonald Islands (to Australia) | extant | native | yes | |||
High Seas | extant | native | yes | |||
Madagascar | extant | uncertain | ||||
Mozambique | extant | uncertain | ||||
Namibia | extant | native | yes | |||
New Zealand | extant | native | yes | |||
Norfolk Island (to Australia) | extant | uncertain | ||||
Peru | extant | native | yes | |||
South Africa | extant | native | yes | |||
South Georgia & the South Sandwich Islands | extant | native | yes | |||
St Helena (to UK) | extant | uncertain | ||||
Uruguay | extant | native | yes |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Grassland | Subantarctic | major | breeding |
Marine Coastal/Supratidal | Sea Cliffs and Rocky Offshore Islands | major | breeding |
Marine Neritic | Estuaries | major | non-breeding |
Marine Neritic | Macroalgal/Kelp | suitable | non-breeding |
Marine Neritic | Macroalgal/Kelp | suitable | breeding |
Marine Neritic | Pelagic | major | non-breeding |
Marine Neritic | Pelagic | major | breeding |
Marine Neritic | Seagrass (Submerged) | suitable | non-breeding |
Marine Neritic | Seagrass (Submerged) | suitable | breeding |
Marine Neritic | Subtidal Loose Rock/pebble/gravel | suitable | non-breeding |
Marine Neritic | Subtidal Loose Rock/pebble/gravel | suitable | breeding |
Marine Neritic | Subtidal Rock and Rocky Reefs | suitable | non-breeding |
Marine Neritic | Subtidal Rock and Rocky Reefs | suitable | breeding |
Marine Neritic | Subtidal Sandy | suitable | non-breeding |
Marine Neritic | Subtidal Sandy | suitable | breeding |
Marine Neritic | Subtidal Sandy-Mud | suitable | non-breeding |
Marine Neritic | Subtidal Sandy-Mud | suitable | breeding |
Marine Oceanic | Epipelagic (0-200m) | major | non-breeding |
Marine Oceanic | Epipelagic (0-200m) | major | breeding |
Marine Oceanic | Mesopelagic (200-1000m) | major | non-breeding |
Marine Oceanic | Mesopelagic (200-1000m) | major | breeding |
Altitude | 0 - 300 m | 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 | ||||||
|
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Biological resource use | Fishing & harvesting aquatic resources - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
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Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Causing/Could cause fluctuations | Medium Impact: 6 | ||||||
|
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Geological events | Volcanoes | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Minority (<50%) | Negligible declines | Past Impact | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Neovison vison | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Rapid Declines | Medium Impact: 6 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Black-browed Albatross Thalassarche melanophris. Downloaded from
https://datazone.birdlife.org/species/factsheet/black-browed-albatross-thalassarche-melanophris on 25/11/2024.
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 25/11/2024.