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Mergellus albellus 

Scope: Global
Status_ne_offStatus_dd_offStatus_lc_onStatus_nt_offStatus_vu_offStatus_en_offStatus_cr_offStatus_ew_offStatus_ex_off

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Anseriformes Anatidae

Scientific Name: Mergellus albellus
Species Authority: (Linnaeus, 1758)
Regional Assessments:
Common Name(s):
English Smew
Synonym(s):
Mergus albellus AERC TAC (2003)
Mergus albellus albellus Cramp and Simmons (1977-1994)
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. Lynx Edicions BirdLife International.

Assessment Information [top]

Red List Category & Criteria: Least Concern ver 3.1
Year Published: 2015
Date Assessed: 2012-05-03
Assessor(s): BirdLife International
Reviewer(s): Butchart, S.
Contributor(s): Pihl, S.
Facilitator/Compiler(s): Ekstrom, J., Butchart, S., Malpas, L. & Symes, A.
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). Despite the fact that the population trend appears to be decreasing, the decline is not believed to be sufficiently rapid to approach the thresholds for Vulnerable under the population trend criterion (>30% decline over ten years or three generations). The population size is very 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). For these reasons the species is evaluated as Least Concern.
Previously published Red List assessments:

Geographic Range [top]

Countries occurrence:
Native:
Afghanistan; Albania; Austria; Azerbaijan; Belarus; Belgium; Bosnia and Herzegovina; Bulgaria; China; Croatia; Czech Republic; Denmark; Egypt; Estonia; Finland; France; Germany; Greece; Hungary; India; Iran, Islamic Republic of; Iraq; Ireland; Italy; Japan; Kazakhstan; Korea, Democratic People's Republic of; Korea, Republic of; Kyrgyzstan; Latvia; Liechtenstein; Lithuania; Luxembourg; Macedonia, the former Yugoslav Republic of; Moldova; Mongolia; Montenegro; Nepal; Netherlands; Norway; Pakistan; Poland; Romania; Russian Federation; Serbia (Serbia); Slovakia; Slovenia; Spain; Sweden; Switzerland; Syrian Arab Republic; Taiwan, Province of China; Tajikistan; Turkey; Turkmenistan; Ukraine; United Kingdom; Uzbekistan
Vagrant:
Algeria; Canada; Cyprus; Gibraltar; Hong Kong; Iceland; Israel; Jordan; Libya; Malta; Myanmar; Palestinian Territory, Occupied; Portugal; Saudi Arabia; Tunisia; United States
Additional data:
Continuing decline in area of occupancy (AOO):Unknown
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:1900000
Continuing decline in extent of occurrence (EOO):UnknownExtreme fluctuations in extent of occurrence (EOO):No
Continuing decline in number of locations:Unknown
Extreme fluctuations in the number of locations:No
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:The global population is estimated to number > c.130,000 individuals (Wetlands International 2006), while the population in Korea has been estimated at c.50-10,000 wintering individuals (Brazil 2009).

Trend Justification:  The population is suspected to be much affected by availability of nest sites in suitable habitat. Populations are also subject to hunting pressure during migration and have been affected by pollution from oil spills (del Hoyo et al. 1992).
Current Population Trend:Decreasing
Additional data:
Continuing decline of mature individuals:Unknown
Extreme fluctuations:NoPopulation severely fragmented:No
Continuing decline in subpopulations:Unknown
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:No

Habitat and Ecology [top]

Habitat and Ecology:Behaviour This species is highly migratory (del Hoyo et al. 1992), often resting and feeding on inland waterbodies when on passage (Kear 2005b). It arrives on the breeding grounds from April (Kear 2005b) or early-May and breeds from mid-May onwards (Madge and Burn 1988) in single pairs or loose groups (del Hoyo et al. 1992). Males gather in large flocks close to the breeding grounds after mating to undergo a flightless moulting period (Madge and Burn 1988). The species then leaves the breeding grounds in early-September and October (Madge and Burn 1988, Kear 2005b). Outside of the breeding season the species is highly gregarious and occurs in small or large flocks (Kear 2005b) usually not exceeding 100 individuals, although larger gatherings may form at major passage waters during migration (Madge and Burn 1988) and flocks of over 10,000 have been recorded during the winter (Kear 2005b). The species feeds diurnally (Madge and Burn 1988) by diving to depths of 1-4 m (Kear 2005b) and forms gregarious nocturnal roosts (Kear 2005b). Habitat Breeding It breeds on freshwater oligotrophic lakes, pools (del Hoyo et al. 1992, Kear 2005b), oxbow lakes (Kear 2005b), backwaters of large slow-flowing rivers (del Hoyo et al. 1992, Snow and Perrins 1998, Kear 2005b), muskegs (bogs) (del Hoyo et al. 1992, Kear 2005b) and flooded riverside woods (Johnsgard 1978, Snow and Perrins 1998) in the coniferous and mixed deciduous/evergreen forest zones (del Hoyo et al. 1992, Snow and Perrins 1998). It shows a preference for shallow water (Johnsgard 1978) up to 4 m (Kear 2005b) (maximum 6 m) deep (Snow and Perrins 1998), and requires mature broadleaved trees (e.g. oaks, willows and aspens) with holes in which to nest (Johnsgard 1978). Non-breeding The species overwinters on large freshwater lakes (del Hoyo et al. 1992) and reservoirs (Johnsgard 1978), ice-free rivers (Kear 2005b), brackish coastal lagoons, estuaries (del Hoyo et al. 1992) and sheltered coastal bays (Madge and Burn 1988) (although rarely on the open sea) (del Hoyo et al. 1992), often resting and feeding on small bodies of water or small streams when on passage (Kear 2005b). Diet During the breeding season its diet consists predominantly of benthic aquatic invertebrates such as adult and larval insects (del Hoyo et al. 1992, Kear 2005b), crustaceans, molluscs and polycheate worms (Kear 2005b), as well as amphibians (del Hoyo et al. 1992), fish (Kear 2005b) and plant matter (del Hoyo et al. 1992) (seeds, leaves and roots) (Kear 2005b). During the winter and in early spring however the species mainly feeds on fish (del Hoyo et al. 1992). Breeding site The species nests in tree hollows (del Hoyo et al. 1992) up to 10 m or more above the ground (Kear 2005b) (especially those excavated by Black Woodpeckers Dryocopus martius) (Madge and Burn 1988) in mature broadleaved trees (e.g. oak, willow or aspen) (Johnsgard 1978). It may also nest in artificial nest boxes (del Hoyo et al. 1992, Kear 2005b), especially those erected to attract Common Goldeneye Bucephala clangula (Madge and Burn 1988, Snow and Perrins 1998).
Systems:Terrestrial; Freshwater; Marine
Continuing decline in area, extent and/or quality of habitat:Unknown
Generation Length (years):5.7
Movement patterns:Full Migrant
Congregatory:Congregatory (and dispersive)

Threats [top]

Major Threat(s): Where it occurs in large numbers on coastal waters the species is particularly vulnerable to oil pollution (del Hoyo et al. 1992). Populations declined in Europe throughout the 19th and 20th centuries due to habitat degradation and loss (e.g. the loss of mature trees in river valleys as a result of logging, conversion to agriculture and river canalisation) (Kear 2005b). The species has also suffered local declines as a result of predation by American mink Neovison vison (Kear 2005b), and is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Utilisation The species is susceptible to a certain amount of hunting pressure when on passage and during the winter (del Hoyo et al. 1992).

Citation: BirdLife International. 2015. Mergellus albellus. The IUCN Red List of Threatened Species 2015: e.T22680465A67277549. . Downloaded on 31 August 2016.
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