LC
Black-browed Albatross Thalassarche melanophris



Taxonomy

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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - -

Red List history
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
Species attributes

Migratory status full migrant Forest dependency does not normally occur in forest
Land-mass type shelf island
Average mass -
Range

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 -
Population
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 distribution
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

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Argentina Frente Península Valdés
Argentina Talud Agujero Azul
Australia Macquarie Island
Chile Guamblin Island
Chile Isla Diego de Almagro
Chile Islas Diego Ramírez y Rocas Norte
Chile Islas Ildefonso
Chile Islote Albatros - Seno Almirantazgo
Chile Islote Leonard
Chile Islotes Evangelistas
Chile Quinchele Inland and surrouding sea
Falkland Islands (Malvinas) Beauchêne Island
Falkland Islands (Malvinas) Bird Island
Falkland Islands (Malvinas) Hope Harbour, West Falkland
Falkland Islands (Malvinas) Jason Islands Group
Falkland Islands (Malvinas) Keppel Island
Falkland Islands (Malvinas) New Island Group
Falkland Islands (Malvinas) Saunders Island
Falkland Islands (Malvinas) West Point Island Group
French Southern Territories Îles Nuageuses and Île Clugny
Heard Island and McDonald Islands (to Australia) Heard and McDonald Islands
High Seas Atlantic, Southwest 37 - Marine
High Seas Atlantic, Southwest 40 - Marine
New Zealand Antipodes (offshore)
New Zealand Antipodes Islands
New Zealand Campbell (offshore)
New Zealand Campbell Islands
New Zealand Campbell Islands (nearshore)
New Zealand East Coast South Island (offshore)
New Zealand Kaikoura (offshore)
Peru Reserva Nacional de Paracas
South Georgia & the South Sandwich Islands South Georgia - mainland, islands, islets and stacks

Habitats & altitude
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  

Threats & impact
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
Stresses
Species mortality
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
Stresses
Species mortality
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
Stresses
Species disturbance, Reduced reproductive success
Climate change & severe weather Habitat shifting & alteration Timing Scope Severity Impact
Ongoing Majority (50-90%) Causing/Could cause fluctuations Medium Impact: 6
Stresses
Reduced reproductive success
Geological events Volcanoes Timing Scope Severity Impact
Past, Likely to Return Minority (<50%) Negligible declines Past Impact
Stresses
Species disturbance, Reduced reproductive success
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
Stresses
Reduced reproductive success
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
Stresses
Reduced reproductive success

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.