Taxonomic source(s)
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.
Livezey, B. C. 1995. Phylogeny and evolutionary ecology of modern seaducks (Anatidae: Mergini). Condor 97(1): 233-255.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2021 | Near Threatened | A2bce+3bce+4bce |
2018 | Near Threatened | A2bce+3bce+4bce |
2016 | Near Threatened | A2bce+3bce+4bce |
2013 | Near Threatened | A2bce+3bce+4bce |
2012 | Near Threatened | A2bce+3bce+4bce |
2008 | Not Recognised | |
2004 | Not Recognised | |
2000 | Not Recognised | |
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) | 17,700,000 km2 | medium |
Extent of Occurrence (non-breeding) | 46,900,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 350000-560000 mature individuals | poor | estimated | 2006 |
Population trend | decreasing | - | inferred | 2014-2030 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Generation length | 5.3 years | - | - | - |
Population justification: The total population is estimated to number c.530,000-830,000 individuals (Delany and Scott 2006), probably including c.350,000-560,000 mature individuals, on the basis that they account for around 2/3 of the population. Partners in Flight (2019) estimate the population at ~500,000, within the range stipulated above.
Trend justification: This species is thought to be declining in western Alaska and to be stable on the Arctic coastal plain (per Sea Duck Joint Venture 2003). Numbers also appear to be declining in the Atlantic flyway, whereas no statistically significant population trend is apparent in the results of a fixed-wing aerial survey covering the Atlantic coast for the period 1991-1999 (Sea Duck Joint Venture 2003). Data from the U.S. Fish and Wildlife Service/Canadian Wildlife Service breeding waterfowl survey indicate that the combined population of all three scoter species along survey transects in the western boreal forest may have declined by as much as 75% since the 1950s (Sea Duck Joint Venture 2003). Estimates from a more recent survey indicate that the breeding population in western Alaska is currently c.160,000 birds and appears to have increased slightly since the survey was initiated in 2004 (R. Stehn per T. Bowman in litt. 2012). Mid-winter inventory data do not indicate any trends on the Pacific coast and only show a weak decline on the Atlantic coast although dramatic local increases are noted in the Lower New York Bay (Ramírez-Garofalo 2020). However, these surveys are said to track scoter populations poorly and all three species are combined in one count (Sea Duck Joint Venture 2003). Trends are apparently uncertain in far north-east Asia (see Delany and Scott 2006); thus more research is required. Limited data and anecdotal evidence from South Korea suggests that the species has declined substantially as a wintering species since the 1960s and 1970s (N. Moores in litt. 2012). Rosenberg et al. (2019) suggest a decline in mature individuals of 400,731 between 1970 and 2017, a decline of ~56% across the period and ~24% across three generation lengths (~16 years) (Partners in Flight 2019). As a result of this estimate and the mixed evidence presented above, the population is suspected to be undergoing a moderately rapid decline (i.e. 20-29% over three generations).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Canada | extant | native | yes | yes | yes | |
China (mainland) | extant | native | yes | |||
Japan | extant | native | yes | |||
Mexico | extant | native | yes | |||
North Korea | extant | native | yes | |||
Russia | extant | native | yes | yes | yes | |
Russia (Asian) | extant | native | yes | |||
South Korea | extant | native | yes | |||
St Pierre and Miquelon (to France) | extant | native | yes | yes | ||
USA | extant | native | yes | yes | yes |
Country/Territory | IBA Name |
---|---|
Canada | Albany River Estuary and Assoc. Coastline |
Canada | Ekwan to Lakitusaki Shores |
Canada | Longridge Point and Associated Coastline |
Canada | Nicolet et Baie-du-Fèbvre |
Canada | Northeast James Bay Coast |
Canada | Pen Islands |
Canada | Point Lepreau/Maces Bay |
Canada | Restigouche River Estuary |
Canada | Shagamu River and Area |
Russia (Asian) | Bol'shaya River Estuary |
Russia (Asian) | Karaginskiy Island |
Russia (Asian) | Lebediny refuge (Markovo depression) |
Russia (Asian) | Lesser Kuril Ridge and Kunashir Island |
Russia (Asian) | Nevskoye Lake |
Russia (Asian) | North-east Sakhalin lagoons |
USA | Central Yukon - Kuskokwim |
USA | Kachemak Bay |
USA | Kuskokwim Bay, marine |
USA | Kuskokwim River Delta |
USA | Kvichak Bay |
USA | Marmot Bay |
USA | Nelson Lagoon-Mud Bay |
USA | Nushagak Bay |
USA | Nushagak Bay, marine |
USA | Port Heiden |
USA | Port Moller-Herendeen Bay |
USA | Prince William Sound |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Marine Neritic | Macroalgal/Kelp | major | non-breeding |
Marine Neritic | Pelagic | suitable | non-breeding |
Marine Neritic | Seagrass (Submerged) | major | non-breeding |
Marine Neritic | Subtidal Loose Rock/pebble/gravel | major | non-breeding |
Marine Neritic | Subtidal Rock and Rocky Reefs | major | non-breeding |
Marine Neritic | Subtidal Sandy | major | non-breeding |
Marine Neritic | Subtidal Sandy-Mud | major | non-breeding |
Shrubland | Boreal | suitable | breeding |
Wetlands (inland) | Tundra Wetlands (incl. pools and temporary waters from snowmelt) | 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%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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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 | ||||
Future | Majority (50-90%) | Slow, Significant Declines | Low Impact: 4 | ||||||
|
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Climate change & severe weather | Other impacts | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Energy production & mining | Oil & gas drilling | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
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Invasive and other problematic species, genes & diseases | Viral/prion-induced diseases - Avian Influenza Virus (H5N1 subtype) | Timing | Scope | Severity | Impact | ||||
Future | Minority (<50%) | Rapid Declines | Low Impact: 4 | ||||||
|
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Pollution | Agricultural & forestry effluents - Nutrient loads | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
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Pollution | Industrial & military effluents - Oil spills | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Transportation & service corridors | Shipping lanes | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Sport hunting/specimen collecting | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Black Scoter Melanitta americana. Downloaded from
https://datazone.birdlife.org/species/factsheet/black-scoter-melanitta-americana on 23/11/2024.
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 23/11/2024.