IUCN Red List history
| Year | Category |
|---|---|
| 2012 | Least Concern |
| 2009 | Least Concern |
| 2008 | Least Concern |
| 2004 | Least Concern |
| 2000 | Lower Risk/Least Concern |
| 1996 | Vulnerable |
| 1994 | Vulnerable |
| 1988 | Lower Risk/Least Concern |
Species attributes
| Migratory status | full migrant | Forest dependency | Does not normally occur in forest |
| Land mass type | continent |
Average mass | - |
Distribution
| Estimate | Data quality | |
|---|---|---|
| Extent of Occurrence breeding/resident (km2) | 568,000 | medium |
| Extent of Occurrence non-breeding (km2) | 754,000 | medium |
| Number of locations | - | |
| Fragmentation | - |
Population & trend
| Estimate | Data quality | Derivation | Year of estimate | |
|---|---|---|---|---|
| No. of mature individuals | poor | Estimated | 2009 | |
| Population trend | Decreasing | - | ||
| Number of subpopulations | - | - | - | |
| Largest subpopulation | - | - | - | |
| Generation length (yrs) | 8.6 | - | - | - |
| Population justification: The global population is estimated at c.330,000-390,000 individuals (Wetlands International 2006). Although a massive decline of over 90% in breeding birds has been reported in the Yukon-Kuskokwim Delta, Alaska (Stehn et al. 1993), no similar decline has been noted in Russia and 155,000 birds were counted on its wintering grounds in 1995 (Balogh 1996). The population in Russia has more recently been estimated at c.100-10,000 breeding pairs and c.50-1,000 wintering individuals (Brazil 2009) although there is a degree of uncertainty in these estimates. Surveys in north Alaska during 1993-1995 indicated 7,000-10,000 breeding birds, with no indication of a declining trend. Recent survey work has discovered a huge concentration of this species in the Bering sea south of St Lawrence Island (Petersen et al. 1999). Estimates suggest that at least 333,000 birds winter in single-species flocks in the pack ice of the Bering Sea (Petersen et al. 1999), representing a total population estimate similar to that of c.400,000 individuals made during the 1970s. | ||||
| Trend justification: The overall trend is suspected to be decreasing (Wetlands International 2006). | ||||
Country/Territory distribution
| Country/Territory | Occurrence status | Extinct | Breeding | Non-breeding | Passage |
|---|---|---|---|---|---|
| Norway | Vagrant | No | |||
| Russia (Asian) | Native | No | Yes | ||
| Russia (Central Asian) | Vagrant | No | |||
| USA | Native | No | Yes |
Important Bird Areas where this species has triggered the IBA criteria
| Country/Territory | IBA Name | IBA link |
|---|---|---|
| Russia (Asian) | Chaun delta | ![]() |
| Russia (Asian) | Inchoun and Uelen lagoons | ![]() |
| Russia (Asian) | Indigirka delta | ![]() |
| Russia (Asian) | Sireniki coast | ![]() |
| Russia (Asian) | West Chaun plain | ![]() |
Habitats & altitude
| Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
|---|---|---|---|
| Marine Neritic | Macroalgal/Kelp | major | breeding |
| Marine Neritic | Macroalgal/Kelp | major | non-breeding |
| Marine Neritic | Pelagic | suitable | non-breeding |
| Marine Neritic | Seagrass (Submerged) | major | breeding |
| Marine Neritic | Seagrass (Submerged) | major | non-breeding |
| Marine Neritic | Subtidal Loose Rock/pebble/gravel | major | non-breeding |
| Marine Neritic | Subtidal Loose Rock/pebble/gravel | major | breeding |
| Marine Neritic | Subtidal Rock and Rocky Reefs | major | non-breeding |
| Marine Neritic | Subtidal Rock and Rocky Reefs | major | breeding |
| Marine Neritic | Subtidal Sandy | major | breeding |
| Marine Neritic | Subtidal Sandy | major | non-breeding |
| Marine Neritic | Subtidal Sandy-Mud | major | non-breeding |
| Marine Neritic | Subtidal Sandy-Mud | major | breeding |
| Wetlands (inland) | Tundra Wetlands (incl. pools and temporary waters from snowmelt) | major | breeding |
| Altitude | 0 - 0 m | Occasional altitudinal limits |
Threats & impact
| Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
|---|---|---|---|---|---|---|---|---|---|
| Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
| Future | Whole (>90%) | Unknown | Unknown | ||||||
| |||||||||
Utilisation
| Purpose | Primary form used | Life stage used | Source | Scale | Level | Timing |
|---|---|---|---|---|---|---|
| Food (human) | Whole | Adults and juveniles | Wild | Subsistence, National | Non-trivial | Recent |
| Food (human) | Whole | Eggs | Wild | Subsistence, National | Non-trivial | Recent |
| Pets | Whole | Adults and juveniles | Wild | International | Non-trivial | Recent |
Recommended citation
BirdLife International (2013) Species factsheet: Somateria fischeri. Downloaded from
http://www.birdlife.org on 19/06/2013.
Recommended citation for factsheets for more than one species: BirdLife International (2013) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 19/06/2013.
This information is based upon, and updates, the information published in BirdLife International (2000) Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004) Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.
To provide new information to update this factsheet or to correct any errors, please email BirdLife
To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.
| Key facts | |
|---|---|
| Current IUCN Red List category | Least Concern |
| Family | Anatidae (Ducks, geese and swans) |
| Species name author | (Brandt, 1847) |
| Population size | mature individuals |
| Population trend | Decreasing |
| Distribution size (breeding/resident) | 568,000 km2 |
| Country endemic? | No |
| Links to further information | |
| - Summary information on this species | |
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