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Calidris ferruginea

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Taxonomy [top]

Kingdom Phylum Class Order Family
ANIMALIA CHORDATA AVES CHARADRIIFORMES SCOLOPACIDAE

Scientific Name: Calidris ferruginea
Species Authority: (Pontoppidan 1763)
Common Name/s:
English Curlew Sandpiper
French Bécasseau cocorli

Assessment Information [top]

Red List Category & Criteria: Least Concern     ver 3.1
Year Published: 2009
Assessor/s: BirdLife International
Reviewer/s: Bird, J., Butchart, S.
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 extremely 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.
History:
2008 Least Concern
2004 Least Concern

Geographic Range [top]

Countries:
Native:
Afghanistan; Albania; Algeria; Angola; Anguilla; Antigua and Barbuda; Armenia; Australia; Austria; Azerbaijan; Bahrain; Bangladesh; Barbados; Belarus; Belgium; Benin; Bosnia and Herzegovina; Botswana; British Indian Ocean Territory; Brunei Darussalam; Bulgaria; Burkina Faso; Burundi; Cambodia; Cameroon; Canada; Cape Verde; Central African Republic; Chad; China; Christmas Island; Comoros; Congo; Congo, The Democratic Republic of the; Costa Rica; Côte d'Ivoire; Croatia; Cyprus; Czech Republic; Denmark; Djibouti; Dominica; Egypt; Equatorial Guinea; Eritrea; Estonia; Ethiopia; Finland; France; French Southern Territories (the); Gabon; Gambia; Georgia; Germany; Ghana; Greece; Guadeloupe; Guam; Guinea; Guinea-Bissau; Hong Kong; Hungary; India; Indonesia; Iran, Islamic Republic of; Iraq; Ireland; Israel; Italy; Japan; Jordan; Kazakhstan; Kenya; Korea, Republic of; Kuwait; Kyrgyzstan; Latvia; Lebanon; Liberia; Libyan Arab Jamahiriya; Macedonia, the former Yugoslav Republic of; Madagascar; Malawi; Malaysia; Maldives; Mali; Malta; Martinique; Mauritania; Mauritius; Mayotte; Moldova; Mongolia; Montenegro; Montserrat; Morocco; Mozambique; Myanmar; Namibia; Nepal; Netherlands; New Caledonia; New Zealand; Niger; Nigeria; Norway; Oman; Pakistan; Palau; Palestinian Territory, Occupied; Papua New Guinea; Peru; Philippines; Poland; Portugal; Qatar; Réunion; Romania; Russian Federation; Russian Federation; Russian Federation; Rwanda; Saint Kitts and Nevis; Saint Lucia; Saint Vincent and the Grenadines; Saudi Arabia; Senegal; Serbia; Seychelles; Sierra Leone; Singapore; Slovakia; Solomon Islands; Somalia; South Africa; Spain; Sri Lanka; Sudan; Swaziland; Sweden; Switzerland; Syrian Arab Republic; Taiwan, Province of China; Tajikistan; Tanzania, United Republic of; Thailand; Timor-Leste; Togo; Tunisia; Turkey; Turkmenistan; Uganda; Ukraine; United Arab Emirates; United Kingdom; United States; Uzbekistan; Viet Nam; Western Sahara; Yemen; Zambia; Zimbabwe
Vagrant:
Bermuda; Bhutan; Ecuador; Gibraltar; Grenada; Iceland; Lao People's Democratic Republic; Lesotho; Luxembourg; Marshall Islands; Mexico; Puerto Rico; Saint Pierre and Miquelon; Sao Tomé and Principe; Svalbard and Jan Mayen; Trinidad and Tobago; Virgin Islands, British
Range Map: Click here to open the map viewer and explore range.

Habitat and Ecology [top]

Habitat and Ecology: Behaviour This species is a full migrant, moving long distances by well-travelled routes1, 2. During the autumn migration adults precede the juveniles, with males leaving 3-4 weeks before the females in early-July, and juveniles following 4-6 weeks later1. On this southern migration, the species crosses Europe in July, reaching Africa from mid-July to September1. The return migration to the breeding grounds begins late-April to May, with arrival in the Arctic beginning in early-June, and breeding stretching from June to July1. Many 1st-year birds remain on the wintering grounds, and non-breeding adults remain just south of the breeding grounds in Central Siberia during the summer1. Nest density on the breeding grounds in commonly 1-2 pairs/ha4, but pairs will sometimes nest as close as 200-300 m1. The species is gregarious outside of the breeding season, occurring in small parties or larger flocks of up to several hundreds on the coast, but usually in smaller numbers inland (although gatherings of hundreds can occur locally on passage)3. It forages both diurnally and nocturnally1. Habitat Breeding This species breeds on slightly elevated areas in the lowlands of the high Arctic1, 4 especially on southward-facing slopes4, as well as along the coast and islands of the Arctic Ocean1. It shows a preference for open tundra with marshy, boggy depressions and pools1, 2 from melting permafrost and snow2. Non-breeding In the winter the species chiefly occurs on coastal brackish lagoons, tidal mud- and sandflats, estuaries, saltmarshes1, 2, exposed coral, rocky shores and tidewrack on sandy beaches3, and also inland on the muddy edges of marshes, large rivers and lakes (both saline and freshwater), irrigated land, flooded areas1, dams3 and saltpans10. Diet Breeding On the breeding grounds the diet of this species consists mainly of insects, such as the adults, pupae and larva of Diptera (e.g. midges, craneflies4) and beetles, as well as bugs and leeches1. Non-breeding In the winter its diet consists of polycheate worms, molluscs, crustaceans (such as amphipods, brine shrimps and copepods), and occasionally insects and seeds1. Breeding site The nest is a cup positioned on the margins of marshes or pools, on the slopes of hummock tundra, or on dry patches in Polygonum tundra1.

Systems: Terrestrial; Freshwater; Marine

Threats [top]

Major Threat(s): In China and South Korea important migrational staging areas of this species around the coast of the Yellow Sea are being lost through land reclamation, and degraded as a result of declining river flows (from water abstraction), increased environmental pollution, unsustainable harvesting of benthic fauna and a reduction in the amount of sediment being carried into the area by the Yellow and Yangtze Rivers5, 7, 9. The species is threatened on the south-east coast of India (Point Calimere) by illegal hunting (bird trapping), reservoir and marshland habitat alteration by salt-industries, and habitat degradation by diminishing rainfall (changing the salt regime)6. It is also threatened at Walvis Bay in Namibia, a key wetland site in southern Africa, by habitat degradation (e.g. changes in the flood regime due to road building, and wetland reclamation for suburb and port development), and disturbance from tourism12. This species is susceptible to avian influenza8, 11 and avian botulism13, 14 so may be threatened by future outbreaks of these diseases.

Bibliography [top]

Balachandran, S. 2006. The decline in wader populations along the east coast of India with special reference to Point Calimere, south-east India. In: Boere, G.; Galbraith, C., Stroud, D. (ed.), Waterbirds around the world, pp. 296-301. The Stationary Office, Edinburgh, UK.

Barter, M. 2002. Shorebirds of the Yellow Sea. Wetlands International, Canberra, Australia.

Barter, M. A. 2006. The Yellow Sea - a vitally important staging region for migratory shorebirds. In: Boere, G.; Galbraith, C., Stroud, D. (ed.), Waterbirds around the world, pp. 663-667. The Stationary Office, Edinburgh, UK.

Blaker, D. 1967. An outbreak of Botulinus poisoning among waterbirds. Ostrich 38(2): 144-147.

del Hoyo, J.; Elliott, A.; Sargatal, J. 1996. Handbook of the Birds of the World, vol. 3: Hoatzin to Auks. Lynx Edicions, Barcelona, Spain.

Gaidet, N.; Dodman, T.; Caron, A.; Balança, G.; Desvaux, S.; Goutard, F.; Cattoli, G.; Lamarque, F.; Hagemeijer, W.; Monicat, F. 2007. Avian Influenza Viruses in Water Birds, Africa. Emerging Infectious Diseases 13(4): 626-629.

Johnsgard, P. A. 1981. The plovers, sandpipers and snipes of the world. University of Nebraska Press, Lincoln, U.S.A. and London.

Kelin, C.; Qiang, X. 2006. Conserving migratory shorebirds in the Yellow Sea region. In: Boere, G.; Galbraith, C., Stroud, D. (ed.), Waterbirds around the world, pp. 319. The Stationery Office, Edinburgh, UK.

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.

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

Urban, E. K.; Fry, C. H.; Keith, S. 1986. The birds of Africa vol. II. Academic Press, London.

van Heerden, J. 1974. Botulism in the Orange Free State goldfields. Ostrich 45(3): 182-184.

Wearne, K.; Underhill, L. G. 2005. Walvis Bay, Namibia: a key wetland for waders and other coastal birds in southern Africa. Wader Study Group Bulletin 107: 24-30.

Citation: BirdLife International 2009. Calidris ferruginea. In: IUCN 2011. IUCN Red List of Threatened Species. Version 2011.2. <www.iucnredlist.org>. Downloaded on 21 May 2012.
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