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LC
Mute Swan Cygnus olor

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 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). 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.

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#.
Christidis, L.; Boles, W. E. 2008. Systematics and taxonomy of Australian birds. CSIRO Publishing, Collingwood, Australia.
Cramp, S.; Perrins, C. M. 1977-1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. Oxford University Press, Oxford.
del Hoyo, J.; Collar, N. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.
Turbott, E. G. 1990. Checklist of the birds of New Zealand. Ornithological Society of New Zealand, Wellington.

Population justification
The global population is estimated to number c.600,000-610,000 individuals (Wetlands International 2006), while national population estimates include: <c.100 breeding pairs and <c.1,000 wintering individuals in China; <c.50 individuals on migration and <c.50 wintering individuals in Korea and c.100-10,000 introduced breeding pairs in Japan (Brazil 2009).

Trend justification
The overall population trend is increasing, although some populations may be stable and others have unknown trends (Wetlands International 2006).

Ecology
Behaviour Truly wild populations of this species are migratory (particularly where displaced by cold weather) (del Hoyo et al. 1992, Snow and Perrins 1998) although European and feral populations are essentially sedentary (Johnsgard 1978, del Hoyo et al. 1992, Scott and Rose 1996, Snow and Perrins 1998) or only locally migratory or nomadic (Scott and Rose 1996, Snow and Perrins 1998). The species breeds during the local spring (del Hoyo et al. 1992, Kear 2005a)as isolated pairs in well-defended territories (del Hoyo et al. 1992). After breeding the adults may gather in large concentrations of thousands or more (Johnsgard 1978, Madge and Burn 1988) on selected waters (Madge and Burn 1988) (non-breeders in northern Europe migrating to such gatherings (Snow and Perrins 1998)) between July and August (Scott and Rose 1996) to undergo a flightless moulting period lasting for 6-8 weeks (Kear 2005a). Although not noticeably sociable in many areas during the winter (Johnsgard 1978) the species may flock in groups of several thousands on favoured waters (Johnsgard 1978, Madge and Burn 1988, Scott and Rose 1996). Habitat The species inhabits a variety of lowland freshwater wetlands (del Hoyo et al. 1992) such as shallow lakes (Kear 2005a), ponds (Madge and Burn 1988), lagoons, marshes (del Hoyo et al. 1992), reedbeds (del Hoyo et al. 1992, Snow and Perrins 1998) and slow-flowing rivers (Kear 2005a) (showing a preference for clean, weed-filled streams over larger, polluted rivers) (Johnsgard 1978). It is also common on artificial waterbodies such as reservoirs, gravel-pits, ornamental lakes (del Hoyo et al. 1992), ditches (Snow and Perrins 1998) and canals (Scott and Rose 1996), and will graze on grassland and agricultural land (e.g. arable cereal fields) (Kear 2005a). Moulting congregations of adults and non-breeders (Snow and Perrins 1998) may also utilise brackish or saline habitats (Johnsgard 1978) including brackish marshes (Kear 2005a), estuaries and sheltered coastal sites (del Hoyo et al. 1992) (e.g. brackish lagoons (Kear 2005a) and bays (Madge and Burn 1988)). Diet Its diet consists predominantly of leaves and the vegetative parts of aquatic plants (Johnsgard 1978, del Hoyo et al. 1992) and grasses (del Hoyo et al. 1992) as well as algae (Johnsgard 1978) and grain (del Hoyo et al. 1992), occasionally also taking small amphibians (Johnsgard 1978, del Hoyo et al. 1992) (frogs, toads and tadpoles) (Snow and Perrins 1998) and aquatic invertebrates (e.g. molluscs, insects and worms) (Johnsgard 1978, del Hoyo et al. 1992). Breeding site The nest is a large mound of aquatic vegetation (del Hoyo et al. 1992, Kear 2005a) placed close to or floating on shallow water (del Hoyo et al. 1992, Kear 2005a) or amongst reeds (del Hoyo et al. 1992). Breeding pairs often re-use nesting sites from previous years if the it was successful (Johnsgard 1978). Management information The cyclical removal of adult fish from an artificial waterbody (gravel pit) in the UK resulted in an increase in the growth of submerged aquatic macrophytes and in turn led to an increase in the winter use of the habitat by the species (Giles 1994). The removed fish (dead or alive) were sold to generate funds (Giles 1994). A control of the breeding output of the species (brood reduction) carried out in the Wylye Valley, UK to try to alleviate the species's negative impacts on fisheries (e.g. by overgrazing submergent riverine vegetation) was found to be ineffective as it had an insignificant impact on local population sizes (possibly due to immigration from surrounding areas) (Watola et al. 2003).

Threats
The species suffers heavy losses from lead poisoning due to ingested lead fishing weights (del Hoyo et al. 1992, Kelly and Kelly 2004), lead shot (Spray and Milne 1988) and lead contaminated sediments from mining and smelting activities (Day et al. 2003). Heavy losses have also been recorded from local incidences of copper poisoning (Kobayashi et al. 1992). The ingestion of or entanglement in fishing lines and/or hooks can also cause severe injury or mortality (Kelly and Kelly 2004) as can collisions with overhead lines (del Hoyo et al. 1992). The species may be threatened by future oil spills (which can cause death by oil saturation) (Berglund et al. 1963). The species is also susceptible to avian influenza (Melville and Shortridge 2006)(e.g. strain H5N1) (Nagy et al. 2007) so may be threatened by future outbreaks of the virus.

References
Berglund, B. E.; Curry-Lindahl, K.; Luther, H.; Olsson, V.; Rodke, W.; Sellerberg, G. 1963. Ecological studies on the Mute Swan (Cygnus olor) in southeastern Sweden. Acta Vertebratica 2(2): 1-120.

Brazil, M. 2009. Birds of East Asia: eastern China, Taiwan, Korea, Japan, eastern Russia. Christopher Helm, London.

Day, D. D.; Beyer, W. N.; Hoffman, D. J.; Morton, A.; Sileo, L.; Audet, D. J.; Ottinger, M. A. 2003. Toxicity of lead-contaminated sediment to Mute Swans. Archives of Environmental Contamination and Toxicology 44: 510-522.

del Hoyo, J.; Elliot, A.; Sargatal, J. 1992. Handbook of the Birds of the World, vol. 1: Ostrich to Ducks. Lynx Edicions, Barcelona, Spain.

Delany, S.; Scott, D. 2006. Waterbird population estimates. Wetlands International, Wageningen, The Netherlands.

Giles, N. 1994. Tufted Duck (Aythya fuligula) habitat use and brood survival increases after fish removal from gravel pit lakes. Hydrobiologia 279/280: 387-392.

Johnsgard, P. A. 1978. Ducks, geese and swans of the World. University of Nebraska Press, Lincoln and London.

Kear, J. 2005. Ducks, geese and swans volume 1: general chapters; species accounts (Anhima to Salvadorina). Oxford University Press, Oxford, U.K.

Kelly, A.; Kelly, S. 2004. Fishing tackle injury and blood lead levels in Mute Swans. Waterbirds 27(1): 60-68.

Kobayashi, Y.; Shimada, A.; Umemura, T.; Nagai, T. 1992. An outbreak of copper poisoning in mute swans (Cygnus olor). Journal of Vetinary Medical Science 54(2): 229-233.

Madge, S.; Burn, H. 1988. Wildfowl. Christopher Helm, London.

Melville, D. S.; Shortridge, K. F. 2006. Migratory waterbirds and avian influenza in the East Asian-Australasian Flyway with particular reference to the 2003-2004 H5N1 outbreak. In: Boere, G.; Galbraith, C., Stroud, D. (ed.), Waterbirds around the world, pp. 432-438. The Stationary Office, Edinburgh, UK.

Nagy, A.; Machova, J.; Hornickova, J.; Tomci, M.; Nagl, I.; Horyna, B.; Holko, I. 2007. Highly pathogenic avian influenza virus subtype H5N1 in Mute swans in the Czech Republic. Vetinary Microbiology 120: 9-16.

Scott, D. A.; Rose, P. M. 1996. Atlas of Anatidae populations in Africa and western Eurasia. Wetlands International, Wageningen, Netherlands.

Snow, D. W.; Perrins, C. M. 1998. The Birds of the Western Palearctic vol. 1: Non-Passerines. Oxford University Press, Oxford.

Spray, C. J.; Milne, H. 1988. The incidence of lead poisoning among whooper and mute swans Cygnus cygnus and C. olor in Scotland. Biological Conservation 44: 265-281.

Watola, G. V.; Stone, D. A.; Smith, G. C.; Forrester, G. J.; Coleman, A. E.; Coleman, J. T.; Goulding, M. J.; Robinson, K. A.; Wilsom, T. P. 2003. Analyses of two mute swan populations and the effects of clutch reduction: Implications for population management. Journal of Applied Ecology 40(3): 565-579.

Further web sources of information
Detailed species account from Birds in Europe: population estimates trends and conservation status (BirdLife International 2004)

Detailed species account from Birds in Europe: population estimates, trends and conservation status (BirdLife International 2004)

Explore HBW Alive for further information on this species

Search for photos and videos, and hear sounds of this species from the Internet Bird Collection

Text account compilers
Ekstrom, J., Butchart, S., Malpas, L.

IUCN Red List evaluators
Butchart, S., Symes, A.

Recommended citation
BirdLife International (2014) Species factsheet: Cygnus olor. Downloaded from http://www.birdlife.org on 27/08/2014. Recommended citation for factsheets for more than one species: BirdLife International (2014) IUCN Red List for birds. Downloaded from http://www.birdlife.org on 27/08/2014.

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.

Additional resources for this species

ARKive species - Mute swan (Cygnus olor) 0

Key facts
Current IUCN Red List category Least Concern
Family Anatidae (Ducks, Geese, Swans)
Species name author (Gmelin, 1789)
Population size mature individuals
Population trend Increasing
Distribution size (breeding/resident) 3,000,000 km2
Country endemic? No
Links to further information
- Additional Information on this species