Data Zone
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 |
| Year | Category | Criteria |
|---|---|---|
| 2018 | Vulnerable | A4bd |
| 2016 | Vulnerable | A4bd |
| 2012 | Vulnerable | A4bd |
| 2010 | Vulnerable | A4b,d |
| 2008 | Vulnerable | A4b,d |
| 2007 | Vulnerable | |
| 2005 | Vulnerable | |
| 2004 | Vulnerable | |
| 2003 | Vulnerable | |
| 2000 | Vulnerable | |
| 1996 | Vulnerable | |
| 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) | 128,000,000 km2 | medium |
| Area of Occupancy (breeding/resident) | 1,900 km2 | medium |
| Number of locations | 11-100 | - |
| Severely fragmented? | no | - |
| Estimate | Data quality | Derivation | Year of estimate | |
|---|---|---|---|---|
| Population size | 20100 mature individuals | medium | estimated | 2007 |
| Population trend | decreasing | good | estimated | 1970-2040 |
| Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
| Generation length | 23.3 years | - | - | - |
| Number of subpopulations | 5 | - | - | - |
Population justification:
In 1998, the total annual breeding population was estimated at 8,500 pairs, equivalent to c. 28,000 mature individuals (Gales 1998). However, current estimates are 1,553 pairs on South Georgia (Georgias del Sur) (Poncet et al. 2006), 1,800 pairs on Prince Edward Island (2008, Ryan et al. 2009), c. 1,900 pairs on Marion Island (2013, ACAP 2009), c. 340 pairs on Iles Crozet (CNRS Chinzè Monitoring Database 2010), c. 354 pairs in Iles Kerguelen (CNRS Chinzè Monitoring Database 2011), and 4 pairs on Macquarie Island (DPIWPE 2010, unpublished data), making a total of c. 6,000 annual breeding pairs. Using the same ratio as Gales (1998) for estimating the number of mature individuals, this would equate to approximately 20,100 mature individuals.
Trend justification: At South Georgia, this species has declined by 1.8% per annum over the past 20 years, and there has been an acceleration in the rate of decrease to over 4% per annum since 1997 (Poncet et al. 2006). Overall, the South Georgian population has declined by 30% between 1984-2004 (Poncet et al. 2006), and by 18% between 2004 and 2015 (A. Wolfaardt in litt. 2016). On Bird Island, adult and post-fledging survival has decreased since the mid 1980s (British Antarctic Survey, unpublished data). On the Crozet Islands, the population stabilised following rapid declines during 1970-1986, but is now declining again (Weimerskirch et al. 1997, Delord et al. 2008). Low juvenile recruitment is believed to be delaying recovery (Weimerskirch et al. 2006). On the Prince Edward Islands, the population is now stable (Nel et al. 2002b, 2002c, Crawford et al. 2003, Ryan et al. 2003, 2009). Overall declines are estimated to exceed 30% over 70 years. However, the long generation time of this species makes it difficult to determine the most appropriate trend period for predicting population trends into the future.
| Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
|---|---|---|---|---|---|---|
| Angola | extant | vagrant | ||||
| 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 | |||
| Falkland Islands (Malvinas) | extant | native | yes | |||
| Fiji | extant | vagrant | yes | |||
| French Polynesia | extant | vagrant | ||||
| French Southern Territories | extant | native | yes | |||
| Heard Island and McDonald Islands (to Australia) | extant | native | yes | |||
| High Seas | extant | native | yes | |||
| Italy | extant | vagrant | ||||
| Japan | extant | vagrant | ||||
| Madagascar | extant | native | yes | |||
| Mauritius | extant | vagrant | ||||
| Mozambique | extant | native | yes | |||
| Namibia | extant | native | yes | |||
| New Zealand | extant | native | yes | |||
| Norfolk Island (to Australia) | extant | native | yes | |||
| Panama | extant | vagrant | yes | |||
| Portugal | extant | vagrant | ||||
| Réunion (to France) | extant | vagrant | ||||
| South Africa | extant | native | yes | |||
| South Georgia & the South Sandwich Islands | extant | native | yes | |||
| St Helena (to UK) | extant | native | yes | |||
| Tonga | extant | uncertain | ||||
| Uruguay | extant | native | yes | |||
| USA | extant | vagrant |
| Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
|---|---|---|---|
| Grassland | Subantarctic | 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%) | Rapid Declines | Medium Impact: 7 | ||||||
|
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| 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 | ||||||
|
|||||||||
| Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
| Ongoing | Whole (>90%) | Slow, Significant Declines | Medium Impact: 7 | ||||||
|
|||||||||
| Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Felis catus | 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 - Mus musculus | Timing | Scope | Severity | Impact | ||||
| Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
| Pollution | Garbage & solid waste | Timing | Scope | Severity | Impact | ||||
| Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
| Purpose | Scale |
|---|---|
| Food - human | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Snowy Albatross Diomedea exulans. Downloaded from
https://datazone.birdlife.org/species/factsheet/snowy-albatross-diomedea-exulans 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.