Overview

Distribution

occurs (regularly, as a native taxon) in multiple nations

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National Distribution

Canada

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Transient

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Transient

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Global Range: BREEDING: Eurasia and at least rarely in western and central Aleutians (Amchitka, probably also Adak and elsewhere). NON-BREEDING: Old World. Accidental in northwestern Hawaii. MIGRATION: rarely but regularly on St Lawrence Island, in Pribilofs and western and central Aleutian Islands, and on mainland western Alaska (AOU 1983).

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Physical Description

Size

Length: 20 cm

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
Behaviour This species is a full migrant, travelling overland on a broad front across Europe and the Middle East1. The adults start to move away from the breeding grounds in late-June, with juveniles following in late-August, arriving in tropical Africa from late-July through August to October2. On this southern migration many birds frequent stop-over sites to the north of the Mediterranean (especially in France and Italy), after which they overfly the Sahara1. Spring departure from the wintering grounds begins in late-March to early-April2, with breeding areas starting to be reoccupied from late-April (early June in northern Russia)2, and with breeding occurring between May and mid-July1. Some non-breeding birds may also remain in the south throughout the summer2. The species nests in well-dispersed solitary pairs (from 1-10 pairs per km2 to 50 pairs per km2 in forest tundra)1, but in winter it may occur in small scattered groups or larger flocks (20-50 individuals), and concentrations can exceed 1,000 individuals on migration3. Habitat Breeding During the breeding season this species inhabits open, swampy areas in boreal forest1, scrubland between tundra and coniferous forest with willow, dwarf birch or spruce2, wet heathlands, and extensive mossy, sedgy or grassy marshes2. Non-breeding Outside of the breeding season this species is less associated with woodlands, being more commonly found in open areas such as the margins of inland freshwater lakes and reservoirs1, 4, muddy marshlands, grassy stream banks, sewage farms, wet paddyfields, small temporary pools1, permanent swamps, flooded grassland and irrigation channels3. It rarely occurs in coastal habitats, but may be found along the creeks of saltmarshes and mangrove swamps1. Diet Breeding Whilst on the breeding grounds this species is chiefly carnivorous, taking small insects (up to 2 cm long), especially the aquatic forms such as dytiscid or hydrophilid beetles, Hemiptera and the larvae of Diptera such as midges4. Non-breeding During the non-breeding season the species has a more varied diet consisting of aquatic and terrestrial insects and their larvae, worms, spiders, crustaceans, gastropod molluscs, small fish (up to 2 cm long) and frogs, as well as plant matter such as seeds1, 4. Breeding site The nest is a scrape on the ground amongst dense vegetation1, 2 or raised on a tussock or slight ridge, and can sometimes be surrounded by water2. The species may also nest in trees in the abandoned nests of other species1 such as thrushes2. Management information Intensive grazing of grassland (> 1 cow per hectare) was found to attract a higher abundance of this species in Hungary7.

Systems
  • Terrestrial
  • Freshwater
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Depth range based on 1043 specimens in 1 taxon.

Environmental ranges
  Depth range (m): 0 - 0
 
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Comments: Lakes, ponds, streams, wet meadows, marshes, bogs, shallow pools; frequently in wooded regions; often near dead trees or brush (AOU 1983, Pratt et al. 1987). Edges of ponds in taiga (AOU 1983).

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Migration

Non-Migrant: No. All populations of this species make significant seasonal migrations.

Locally Migrant: No. No populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).

Locally Migrant: Yes. At least some populations of this species make annual migrations of over 200 km.

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Life History and Behavior

Life Expectancy

Lifespan, longevity, and ageing

Maximum longevity: 11.6 years (wild)
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Molecular Biology and Genetics

Molecular Biology

Barcode data: Tringa glareola

The following is a representative barcode sequence, the centroid of all available sequences for this species. 

 
There are 17 barcode sequences available from BOLD and GenBank.  Below is a sequence of the barcode region Cytochrome oxidase subunit 1 (COI or COX1) from a member of the species.  See the BOLD taxonomy browser for more complete information about this specimen and other sequences.
 
BROM147-06|MKP 1458|Tringa glareola| AACCGATGACTATTCTCAACCAATCACAAAGATATCGGCACCCTATACCTAATCTTCGGTGCATGAGCCGGCATAATTGGAACTGCCCTT---AGCCTCCTTATTCGCGCAGAATTAGGTCAACCGGGAACTTTACTAGGAGAC---GACCAAATTTACAATGTAATCGTCACTGCCCATGCCTTCGTAATAATTTTCTTCATAGTAATACCGATCATAATTGGTGGCTTTGGAAATTGACTAGTCCCACTCATA---ATCGGCGCCCCCGACATAGCATTCCCCCGTATAAACAATATAAGCTTTTGACTTCTTCCCCCATCATTCCTACTACTATTAGCATCCTCAACAGTAGAAGCAGGAGCTGGTACAGGATGAACAGTATATCCCCCTCTCGCCGGTAATCTAGCCCATGCTGGTGCCTCAGTAGACTTG---GCCATCTTCTCTCTCCACTTAGCAGGTGTTTCCTCTATTCTAGGTGCTATTAACTTCATCACAACCGCTATTAACATAAAACCCCCAGCCCTATCCCAATACCAAACTCCCCTATTTGTATGATCCGTACTTATTACTGCTGTTCTCCTCTTACTCTCTCTTCCAGTTCTCGCTGCC---GGCATCACTATACTACTAACAGATCGAAACTTAAACACCACATTCTTCGATCCAGCCGGAGGAGGAGACCCAGTCCTATACCAACATCTCTTCTGATTCTTCGGCCACCCAGAAGTTTACATCCTCATTCTACCAGGCTTCGGAATTATCTCCCATGTCGTAGCCTACTATGCAGGTAAAAAA---GAACCATTTGGATATATAGGAATAGTATGAGCTATACTATCCATCGGATTCCTAGGCTTTATCGTATGAGCCCATCACATATTCACAGTAGGG---- 
-- end --

Download FASTA File
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Statistics of barcoding coverage: Tringa glareola

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 17
Species: 18
Species With Barcodes: 1

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Conservation

Conservation Status

Status in Egypt

Regular passage visitor and winter visitor.

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IUCN

Least Concern.

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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2009

Assessor/s
BirdLife International

Reviewer/s
Bird, J., Butchart, S.

Contributor/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
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National NatureServe Conservation Status

Canada

Rounded National Status Rank: NNA - Not Applicable

United States

Rounded National Status Rank: NNA - Not Applicable

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NatureServe Conservation Status

Rounded Global Status Rank: G5 - Secure

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Population

Population
Total regarded as a minimum by Wetlands International (2006).
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Threats

Threats

Major Threats
The species is threatened in some European countries (such as Finland) from exploitation, and peatland drainage and destruction for forestry and agriculture1. The populations in southern Sweden, Germany and Poland have also declined, possibly due to the threats of climatic change1. The species is susceptible to both avian botulism5 and avian malaria6, so may be threatened by future outbreaks of these diseases.
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Wikipedia

Wood Sandpiper

The Wood Sandpiper, Tringa glareola, is a small wader. This Eurasian species is the smallest of the shanks, which are mid-sized long-legged waders of the family Scolopacidae.

Description and systematics

It resembles a longer-legged and more delicate Green (T. ochropus) or Solitary Sandpiper (T. solitaria) with a short fine bill, brown back and longer yellowish legs. It differs from the first of those species in a smaller and less contrasting white rump patch, while the Solitary Sandpiper nas no white rump patch at all.[1]

However, it is not very closely related to these two species. Rather, its closest relative is the Common Redshank (T. totanus), and these two share a sister relationship with the Marsh Sandpiper (T. stagnatilis). These three species are a group of smallish shanks with red or yellowish legs, a breeding plumage that is generally subdued light brown above with some darker mottling and with a pattern of somewhat diffuse small brownish spots on the breast and neck.[2]

Ecology

In non-breeding plumage

The Wood Sandpiper breeds in subarctic wetlands from the Scottish Highlands across Europe and Asia. They migrate to Africa and southern Asia, particularly India. Vagrant birds have been seen as far into the Pacific as the Hawaiian Islands. In Micronesia it is a regular visitor to the Marianas Islands (where flocks of up to 32 birds are reported) and Palau; it is recorded on Kwajalein in the Marshall Islands about once per decade. This species is encountered in the western Pacific region between mid-October and mid-May[3]

This bird is usually found on freshwater during migration and wintering. They forage by probing in shallow water or on wet mud, and mainly eat insects and similar small prey. T. glareola nests on the ground or uses an abandoned old tree nest of another bird, such as the Fieldfare (Turdus pilaris).[1]

The Wood Sandpiper is one of the species to which the Agreement on the Conservation of African-Eurasian Migratory Waterbirds (AEWA) applies.

Widespread, it is considered a Species of Least Concern by the IUCN.[4]

Footnotes

  1. ^ a b Hayman et al. (1986)
  2. ^ Hayman et al. (1986), Pereira & Baker (2005)
  3. ^ Hayman et al. (1986), Wiles et al. (2000), VanderWerf (2006), VanderWerf et al. (2006)
  4. ^ BLI (2008)

References

  • BirdLife International (BLI) (2008). Tringa glareola. In: IUCN 2008. IUCN Red List of Threatened Species. Downloaded on 12 May 2009.
  • Hayman, Peter; Marchant, John & Prater, Tony (1986): Shorebirds: an identification guide to the waders of the world. Houghton Mifflin, Boston. ISBN 0-395-60237-8
  • Pereira, Sérgio Luiz & Baker, Alan J. (2005): Multiple Gene Evidence for Parallel Evolution and Retention of Ancestral Morphological States in the Shanks (Charadriiformes: Scolopacidae). Condor 107(3): 514–526. DOI:10.1650/0010-5422(2005)107[0514:MGEFPE]2.0.CO;2 PDF fulltext
  • VanderWerf, Eric A. (2006): Observations on the birds of Kwajalein Atoll, including six new species records for the Marshall Islands. Micronesica 38(2): 221–237. PDF fulltext
  • VanderWerf, Eric A.; Wiles, Gary J.; Marshall, Ann P. & Knecht, Melia (2006): Observations of migrants and other birds in Palau, April–May 2005, including the first Micronesian record of a Richard's Pipit. Micronesica 39(1): 11-29. PDF fulltext
  • Wiles, Gary J.; Worthington, David J.; Beck, Robert E. Jr.; Pratt, H. Douglas; Aguon, Celestino F. & Pyle, Robert L. (2000): Noteworthy Bird Records for Micronesia, with a Summary of Raptor Sightings in the Mariana Islands, 1988-1999. Micronesica 32(2): 257-284. PDF fulltext
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