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Tringa ochropus

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Taxonomy [top]

Kingdom Phylum Class Order Family
ANIMALIA CHORDATA AVES CHARADRIIFORMES SCOLOPACIDAE

Scientific Name: Tringa ochropus
Species Authority: Linnaeus, 1758
Common Name/s:
English Green Sandpiper
French Chevalier cul-blanc

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 stable, 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; Armenia; Austria; Azerbaijan; Bahrain; Bangladesh; Belarus; Belgium; Benin; Bhutan; Bosnia and Herzegovina; Brunei Darussalam; Bulgaria; Burkina Faso; Burundi; Cambodia; Cameroon; Cape Verde; Central African Republic; Chad; China; Congo; Congo, The Democratic Republic of the; Côte d'Ivoire; Croatia; Cyprus; Czech Republic; Denmark; Djibouti; Egypt; Eritrea; Estonia; Ethiopia; Finland; France; Gabon; Gambia; Georgia; Germany; Ghana; Greece; Guinea; Guinea-Bissau; Hong Kong; Hungary; India; Indonesia; Iran, Islamic Republic of; Iraq; Ireland; Israel; Italy; Japan; Jordan; Kazakhstan; Kenya; Korea, Democratic People's Republic of; Korea, Republic of; Kuwait; Kyrgyzstan; Lao People's Democratic Republic; Latvia; Lebanon; Liberia; Libyan Arab Jamahiriya; Liechtenstein; Lithuania; Luxembourg; Macedonia, the former Yugoslav Republic of; Malawi; Malaysia; Mali; Malta; Mauritania; Mongolia; Montenegro; Morocco; Mozambique; Myanmar; Nepal; Netherlands; Niger; Nigeria; Norway; Oman; Pakistan; Palestinian Territory, Occupied; Philippines; Poland; Portugal; Qatar; Romania; Russian Federation; Russian Federation; Russian Federation; Rwanda; Saudi Arabia; Senegal; Serbia; Sierra Leone; Singapore; Slovakia; Slovenia; Somalia; South Africa; Spain; Sri Lanka; Sudan; Swaziland; Sweden; Switzerland; Syrian Arab Republic; Taiwan, Province of China; Tajikistan; Tanzania, United Republic of; Thailand; Togo; Tunisia; Turkey; Turkmenistan; Uganda; Ukraine; United Arab Emirates; United Kingdom; Uzbekistan; Viet Nam; Yemen; Zambia; Zimbabwe
Vagrant:
Australia; Botswana; Equatorial Guinea; Faroe Islands; Gibraltar; Iceland; Madagascar; Mauritius; Northern Mariana Islands; Saint Helena; Sao Tomé and Principe; Seychelles; Svalbard and Jan Mayen; United States; Western Sahara
Present - origin uncertain:
Palau
Range Map: Click here to open the map viewer and explore range.

Habitat and Ecology [top]

Habitat and Ecology: Behaviour This species is fully migratory and moves overland on a broad front2 with European populations making well-documented stop-overs in Saharan oases1. Southward movements to the wintering grounds occur between June and early November, with the species being present in the north and equatorial tropics from late-August to early-April, and in southern Africa from October to March1, 2. The return passage to northern breeding grounds occurs between late-February and mid-May1, 2, where the species breeds between late April and June1. In mild winters some birds may also remain in the breeding grounds of southern Scandinavia1. The species generally occurs in low concentrations during passage and at stop-over sites, although it may occur in small scattered groups of up to 30 individuals1 in the winter, with aggregations of over 50 being unusual4. Habitat Breeding During the breeding season this species inhabits damp areas in swampy, old pine, spruce or alder woodland and montane forest with many fallen and rotten tree stumps, marshy forest floors and heavy carpets of lichens and mosses, generally in the vicinity of rivers, streams, swamps, ponds, lakes3 and bogs4. Non-breeding Outside of the breeding season this species shows a preference for a wider variety of inland freshwater habitats such as marshes, lake edges, sewage farms, small dams and ponds, ditches, riverbanks and forest streams, often near villages and cultivation1, 2 (although less often in the vicinity of woodland)1. It is also very rarely found in intertidal areas such as creeks and the channels of saltmarches1, 3. Diet The species is omnivorous, although its diet is predominantly made up of aquatic and terrestrial insects4 (e.g. dragonfly larvae, ants, waterbugs, moth larvae, and the adults and larvae of beetles, Diptera and Trichoptera), annelids, small crustaceans, spiders and fish, as well as plant fragments1. Breeding site This species frequently nests high in trees in the abandoned nests of passerine species such as Common Woodpigeon Columba palumbus, thrushes Turdus spp.1, 5, crows, jays and shrikes3, but may also nest in squirrel dreys3, 4, on natural platforms up to 20 m high1, and occasionally on tree stumps or mounds of accumulated pine needles, among branches and tree roots, or amongst fallen trees on the ground3, 4. Management information Unfertilised grasslands with low cattle densities (0.5 cows per hectare) were found to attract a higher abundance of this species in Hungary7.

Systems: Terrestrial; Freshwater

Threats [top]

Major Threat(s): This species is susceptible to avian influenza (strain H5N1) so may be threatened by future outbreaks of the virus6.

Bibliography [top]

Baldi, A.; Batary, B.; Erdos, S. 2005. Effects of grazing intensity on bird assemblages and populations of Hungarian grasslands. Agriculture Ecosystems & Environment 108: 251-263.

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

Hayman, P.; Marchant, J.; Prater, A. J. 1986. Shorebirds. Croom Helm, London.

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

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.

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