Thalassarche melanophris 

Scope: Global
Language: English
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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Procellariiformes Diomedeidae

Scientific Name: Thalassarche melanophris (Temminck, 1828)
Common Name(s):
English Black-browed Albatross
Synonym(s):
Thalassarche melanophris ssp. melanophris — Christidis and Boles (2008)
Thalassarche melanophrys (Temminck, 1828) [orth. error]
Taxonomic Source(s): 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.
Taxonomic Notes: Thalassarche melanophris (del Hoyo and Collar 2014) was previously listed as T. melanophrys.

Identification information: 88 cm. Medium-sized albatross. Dark grey saddle and upperwings contrast strongly with white head, rump and underparts. Underwing is largely white with very broad, rather irregular, black margins. Dark eyebrow and yellow-orange bill with darker red-orange tip. Juveniles and sub-adults have dark, horn-coloured bills with dark tips, grey on head and collar, and dark underwing, which lightens with age. Similar spp. Juveniles can be very similar to juvenile Grey-headed Albatross Thalassarche chrysostoma but show faintly black-tipped bills and darker ridges.

Assessment Information [top]

Red List Category & Criteria: Least Concern ver 3.1
Year Published: 2017
Date Assessed: 2017-10-01
Assessor(s): BirdLife International
Reviewer(s): Symes, A.
Contributor(s): Arata, J., Croxall, J., Huin, N., Misiak, W., Phillips, R., Robertson, G., Stanworth, A., Wolfaardt, A., Seco Pon, J. & Copello, S.
Facilitator/Compiler(s): Anderson, O., Butchart, S., Calvert, R., Small, C., Sullivan, B., Symes, A., Wheatley, H.
Justification:
This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (extent of occurrence <20,000 km2 combined with a declining or fluctuating range size, habitat extent/quality, or population size and a small number of locations or severe fragmentation). The population size is extremely large, and hence does not approach the thresholds for Vulnerable under the population size criterion (<10,000 mature individuals with a continuing decline estimated to be >10% in ten years or three generations, or with a specified population structure). The population trend appears to be increasing, and hence the species does not approach the thresholds for Vulnerable under the population trend criterion (>30% decline over ten years or three generations). For these reasons the species is evaluated as Least Concern.

Previously published Red List assessments:

Geographic Range [top]

Range Description:Thalassarche melanophris has a circumpolar distribution ranging from subtropical to polar waters (ACAP 2009), breeding in the Falkland Islands (Islas Malvinas), Islas Diego Ramirez, Ildefonso, Diego de Almagro, Isla Evangelistas and islets in Tierra del Fuego and in the Mallaganes region (Chile), South Georgia (Georgias del Sur), Crozet and Kerguelen Islands (French Southern Territories), Heard, McDonald and Macquarie Islands (Australia), and Campbell and Antipodes Islands, New Zealand (Croxall and Gales 1998, ACAP 2009). One colony was also recorded on Snares Island in 1986 (ACAP 2009). The total breeding population is estimated at c.700,000 pairs, c.72% at the Falkland Islands (Islas Malvinas), 19% in Chile and 8% at South Georgia (ACAP unpubl. data). The population size is considered to be increasing.
Countries occurrence:
Native:
Angola; Antarctica; Argentina; Australia; Brazil; Chile; Falkland Islands (Malvinas); French Southern Territories; Heard Island and McDonald Islands; Namibia; New Zealand; Peru; South Africa; South Georgia and the South Sandwich Islands; Uruguay
Vagrant:
Denmark; Fiji
Present - origin uncertain:
Bouvet Island; Ecuador; French Polynesia; Madagascar; Mozambique; Norfolk Island; Saint Helena, Ascension and Tristan da Cunha
Additional data:
Continuing decline in area of occupancy (AOO):Unknown
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:177000000
Continuing decline in extent of occurrence (EOO):UnknownExtreme fluctuations in extent of occurrence (EOO):No
Number of Locations:10Continuing decline in number of locations:Unknown
Extreme fluctuations in the number of locations:No
Upper elevation limit (metres):300
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population: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).
Current Population Trend:Increasing
Additional data:
Number of mature individuals:1400000Continuing decline of mature individuals:No
Extreme fluctuations:NoPopulation severely fragmented:No
Continuing decline in subpopulations:Unknown
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:Yes

Habitat and Ecology [top]

Habitat and Ecology:Behaviour This is a colonial, annually breeding species, although only 75% of successful breeders and 67% of failed breeders breed the following year. Individuals arrive at colonies in September, laying in early October with chicks hatching in December and fledging between April and May. Immature birds begin to return to land at the age of two with the numbers of returning birds increasing up to the age of six. The median age of first breeding is 10 years (range 8-13) (ACAP 2009). During incubation, breeding birds tend to remain in areas adjacent to or to the north of their colonies in the shelf, shelf-break and shelf-slope waters (ACAP 2009). At Campbell Island, Black-browed Albatross show a unique bimodal foraging strategy, alternating between short trips to shelf areas around the breeding site and long trips to the Polar Front (Waugh et al. 1999). Birds foraging over the Benguela Current during the winter also showed a bimodal feeding strategy, alternating trips over deep, oceanic waters with trips over the continental shelf (Petersen et al. 2008). During incubation on South Georgia, satellite tracking reveals males and females forage in different areas with almost no overlap (Phillips et al. 2004). After breeding, birds from the Falkland Islands (Islas Malvinas) winter on the Patagonian Shelf (N. Huin in litt 2008) and estuaries in Buenos Aires province (Río de la Plata and El Rincón) (Copello et al. 2013), whereas birds from South Georgia predominantly migrate to South African waters, spending the first half of the winter in the highly productive Benguela Current (Phillips et al. 2005). Black-browed Albatross from Chile make use of the Chilean Shelf, the Patagonian Shelf, and some spend the non-breeding season around north New Zealand. Habitat Breeding The species nests colonially on steep slopes with tussock grass, sometimes on cliff terraces, but the largest colonies in the Falklands (Islas Malvinas) are on flat ground along the shore line. Diet It feeds mainly on crustaceans, fish and squid, and also on carrion and fishery discards (Cherel et al. 2002, Arata et al. 2003, Xavier et al. 2003, Mariano Jelicich et al. 2014). A Wilson’s Storm-petrel was recorded in the stomach contents of a bycaught individual on the Patagonian Shelf (Seco Pon and Gandini 2008), and while various Sphenisciformes and Procellariiformes have been found in the stomachs of albatrosses, penguins tend to be recorded more frequently, although none are typical prey items (Seco Pon and Gandini 2008). The exact composition of its diet varies depending on locality and year (ACAP 2009). Foraging Range During chick-rearing, breeding T. melanophrys initially stay in shelf to shelf-slope areas very close to their colonies (within c. 500 km). Later, birds from Chile and South Georgia (Islas Georgias del Sur) may also travel up to c. 3,000 km from their breeding sites, especially to the Antarctic Peninsula and South Orkney Islands, but birds from the Falkland Islands (Islas Malvinas) and Kerguelen continue to remain close to their colonies (ACAP 2009). During the non-breeding period adult birds from the Falkland Islands (Islas Malvinas) dispersed north of their colonies up to southern Brazil (Copello et al. 2013).

Systems:Terrestrial; Marine
Continuing decline in area, extent and/or quality of habitat:Unknown
Generation Length (years):21.5
Movement patterns:Full Migrant
Congregatory:Congregatory (and dispersive)

Threats [top]

Major Threat(s): The species is threatened by longline fishing effort and/or the development of new longline fisheries over much of the Patagonian Shelf, around South Georgia, off the southern African coast, and in the Southern Ocean (Tuck and Polacheck 1997, Prince et al. 1998, Schiavini et al. 1998, Stagi et al. 1998). Indeed, it is one of the most frequently killed species in many longline fisheries including tuna longliners off southern Africa, the pelagic longline swordfish fishery off Chile and Argentine longliners targeting toothfish and kingclip on the Patagonian shelf (Murray et al. 1993, Gales et al. 1998, Ryan and Boix-Hinzen 1998, Schiavini et al. 1998, Stagi et al. 1998, Ryan et al. 2002 Reid and Sullivan 2004, Bugoni et al. 2008, Favero et al. 2013). Capture rates can vary greatly according to season, number of hooks and type of longline (Bugoni et al. 2008). Mortality in trawl fisheries has also been identified as a major source of mortality for this species over the Patagonian Shelf (Sullivan and Reid 2002, Favero et al. 2011, Seco Pon et al. 2015) and South Africa (Watkins et al. 2007), and was previously estimated to result in a minimum 5,000 individuals killed per annum across the deep-water hake trawl fishery in south African waters during winter (Watkins et al. 2008). but this threat has since been significantly reduced due largely to the introduction and use of mitigation measures (Maree et al. 2014).
Recent large-scale volcanic eruptions at Heard Island (2003-2004 in particular) may have caused most birds to desert nesting sites (ACAP 2009). The explosion in European rabbit Oryctolagus cuniculus numbers on Macquarie Island since 1999 has led to an extensive destruction of habitat and soil erosion at nesting sites. An eradication programme targeting rodents commenced in 2010 and has been successfully completed (A. Wolfaardt in litt. 2016). Cats (Felis catus) are thought to impact upon colonies on the Kerguelen Islands at Jeanne d'Arc Peninsula (ACAP 2009).

Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
CMS Appendix II and ACAP Annex 1. It is monitored at South Georgia, Kerguelen, Campbell, Diego Ramirez and the Falkland Islands (Islas Malvinas). Most breeding sites are reserves. Heard and McDonald, Macquarie, and the New Zealand islands are World Heritage Sites. An initial census of Chilean islands has been completed (Lawton et al. 2004).  Mitigation measures have significantly reduced the mortality caused by trawl fishing in South Africa (Maree et al. 2014). An eradication programme targeting rodents commenced in 2010 and has been successfully completed (A. Wolfaardt in litt. 2016).

Conservation Actions Proposed
Continue monitoring and research programmes at all sites. Conduct complete censuses at all sites at regular intervals (South Georgia, Chile, Falkland Islands [Islas Malvinas] and French Southern Territories). Assess the impact of trawl fisheries bycatch. Continue to develop mitigation strategies for trawl fisheries, notably on the Patagonian Shelf. Promote adoption of a) monitoring of seabirds bycatch associated with longline fishing and b) best-practice mitigation measures in all fisheries within the species's range, including via intergovernmental mechanisms under the auspices of ACAP, FAO and Regional Fisheries Management Organisations such as CCAMLR and the tuna commissions of the Atlantic Ocean (ICCAT).

Classifications [top]

4. Grassland -> 4.3. Grassland - Subantarctic
suitability:Suitable season:breeding major importance:Yes
9. Marine Neritic -> 9.1. Marine Neritic - Pelagic
suitability:Suitable season:breeding major importance:Yes
9. Marine Neritic -> 9.1. Marine Neritic - Pelagic
suitability:Suitable season:non-breeding major importance:Yes
9. Marine Neritic -> 9.2. Marine Neritic - Subtidal Rock and Rocky Reefs
suitability:Suitable season:breeding major importance:No
9. Marine Neritic -> 9.2. Marine Neritic - Subtidal Rock and Rocky Reefs
suitability:Suitable season:non-breeding major importance:No
9. Marine Neritic -> 9.3. Marine Neritic - Subtidal Loose Rock/pebble/gravel
suitability:Suitable season:breeding major importance:No
9. Marine Neritic -> 9.3. Marine Neritic - Subtidal Loose Rock/pebble/gravel
suitability:Suitable season:non-breeding major importance:No
9. Marine Neritic -> 9.4. Marine Neritic - Subtidal Sandy
suitability:Suitable season:breeding major importance:No
9. Marine Neritic -> 9.4. Marine Neritic - Subtidal Sandy
suitability:Suitable season:non-breeding major importance:No
9. Marine Neritic -> 9.5. Marine Neritic - Subtidal Sandy-Mud
suitability:Suitable season:breeding major importance:No
9. Marine Neritic -> 9.5. Marine Neritic - Subtidal Sandy-Mud
suitability:Suitable season:non-breeding major importance:No
9. Marine Neritic -> 9.7. Marine Neritic - Macroalgal/Kelp
suitability:Suitable season:breeding major importance:No
9. Marine Neritic -> 9.7. Marine Neritic - Macroalgal/Kelp
suitability:Suitable season:non-breeding major importance:No
9. Marine Neritic -> 9.9. Marine Neritic - Seagrass (Submerged)
suitability:Suitable season:breeding major importance:No
9. Marine Neritic -> 9.9. Marine Neritic - Seagrass (Submerged)
suitability:Suitable season:non-breeding major importance:No
9. Marine Neritic -> 9.10. Marine Neritic - Estuaries
suitability:Suitable season:non-breeding major importance:Yes
10. Marine Oceanic -> 10.1. Marine Oceanic - Epipelagic (0-200m)
suitability:Suitable season:breeding major importance:Yes
10. Marine Oceanic -> 10.1. Marine Oceanic - Epipelagic (0-200m)
suitability:Suitable season:non-breeding major importance:Yes
10. Marine Oceanic -> 10.2. Marine Oceanic - Mesopelagic (200-1000m)
suitability:Suitable season:breeding major importance:Yes
10. Marine Oceanic -> 10.2. Marine Oceanic - Mesopelagic (200-1000m)
suitability:Suitable season:non-breeding major importance:Yes
13. Marine Coastal/Supratidal -> 13.1. Marine Coastal/Supratidal - Sea Cliffs and Rocky Offshore Islands
suitability:Suitable season:breeding major importance:Yes
5. Law & policy -> 5.1. Legislation -> 5.1.1. International level

In-Place Research, Monitoring and Planning
  Action Recovery plan:Yes
  Systematic monitoring scheme:Yes
In-Place Land/Water Protection and Management
  Conservation sites identified:Yes, over part of range
  Occur in at least one PA:Yes
  Invasive species control or prevention:Yes
In-Place Species Management
  Successfully reintroduced or introduced beningly:No
  Subject to ex-situ conservation:No
In-Place Education
  Subject to recent education and awareness programmes:No
  Included in international legislation:Yes
  Subject to any international management/trade controls:No
10. Geological events -> 10.1. Volcanoes
♦ timing:Past, Likely to Return ♦ scope:Minority (<50%) ♦ severity:Unknown ⇒ Impact score:Past Impact 
→ Stresses
  • 2. Species Stresses -> 2.2. Species disturbance
  • 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.7. Reduced reproductive success

11. Climate change & severe weather -> 11.3. Temperature extremes
♦ timing:Unknown ♦ scope:Unknown ♦ severity:Unknown ⇒ Impact score:Unknown 
→ Stresses
  • 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.7. Reduced reproductive success

5. Biological resource use -> 5.4. Fishing & harvesting aquatic resources -> 5.4.4. Unintentional effects: (large scale) [harvest]
♦ timing:Ongoing ♦ scope:Majority (50-90%) ♦ severity:No decline ⇒ Impact score:Low Impact: 5 
→ Stresses
  • 2. Species Stresses -> 2.1. Species mortality

8. Invasive and other problematic species, genes & diseases -> 8.1. Invasive non-native/alien species/diseases -> 8.1.2. Named species [ Felis catus ]
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Unknown ⇒ Impact score:Unknown 
→ Stresses
  • 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.7. Reduced reproductive success

8. Invasive and other problematic species, genes & diseases -> 8.1. Invasive non-native/alien species/diseases -> 8.1.2. Named species [ Oryctolagus cuniculus ]
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:No decline ⇒ Impact score:Low Impact: 4 
→ Stresses
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

1. Research -> 1.2. Population size, distribution & trends
1. Research -> 1.5. Threats
3. Monitoring -> 3.1. Population trends

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Citation: BirdLife International. 2017. Thalassarche melanophris. In: The IUCN Red List of Threatened Species 2017: e.T22698375A119512041. . Downloaded on 12 December 2017.
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