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 - Slender-billed Curlew
 - Slender-billed Curlew
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Slender-billed Curlew Numenius tenuirostris Scientific name definitions

Jan Van Gils, Popko Wiersma, Guy M. Kirwan, and Christopher J. Sharpe
Version: 1.0 — Published March 4, 2020
Text last updated January 10, 2018

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Field Identification

36–41 cm; 255–360 g (two specimens); wingspan 80–92 cm. Very pale curlew , with shortish, slim, pointed bill; white or pale buff ground colour of head, neck and breast; lower back, rump, undertail and underwing white; uppertail-coverts white with sparse brown markings; typically has rounded or heart-shaped dark markings on breast and flanks (1). Similar to N. phaeopus, but paler; lacks dark crown-stripe. It is now appreciated that separation from N. arquata can also be difficult (especially versus N. a. orientalis and N. a. suschkini) and many features show some degree of overlap, but the following are now considered particularly critical for identification: colour and pattern of underside of outer primaries, pattern and extent of the tibial feathering and length of exposed tibia, leg colour, pattern of tail feathers, and shape of dark flank markings (1). Female ave­rages larger with longer bill. Non-breeding adult has fewer marks on flanks. Juvenile like adult, but flanks streaked brown.

Systematics History

Monotypic.

Subspecies

Monotypic.

Distribution

SW Siberia; precise breeding range virtually unknown (the only confirmed breeding site, during first quarter of 20th century, was near Tara, N of Omsk) (2). Winters in N Africa and E to Iraq and Persian Gulf. No verified records since 2001; increasingly likely to be extinct.

Habitat

Breeds in extensive peat bogs with some small willow (Salix) and birch (Betula) trees, in habitat transitional from bog to forest, using small islands of dry habitat within large marshes (3). On migration, occurs in coastal lagoons and adjoining saltmarshes, estuaries, inland soda- or saltlakes or (drained) fishponds in steppe area. Winters in coastal bays and lagoons with saltmarshes and temporary inland marshes. Few birds observed in Morocco appear to be habitat generalists, occurring on seashore, in saline and brackish lagoons and estuaries, in temporary and permanent lakes with adjoining marshes, on mudflats, and in sandy grassland and arable fields.

Movement

SW–WSW migration towards Mediterranean, mainly terminating in Atlantic Morocco and in Tunisia, but perhaps formerly also wintered in very small numbers in Netherlands (particularly in the Zuiderzee area) (4, 5, 6); chiefly via Turkmenistan, Caspian steppes, Ukraine, Bulgaria (where more recorded in spring, 20 Mar–18 May, versus autumn, 19 Sept–9 Nov) (7), Romania, former Yugoslavia, S Hungary, Greece and Italy; a second migration route may lead from breeding grounds to Middle East, where wintered in Iraq and also reported to occur in Iran (8), Saudi Arabia, Oman and Yemen (9), with unconfirmed records even further E, in coastal Pakistan and NW India (10). However, many of the published records from the Middle East, especially those from Iran and Turkey, as well as adjacent Greece, are either unquestionably erroneous or, at least, might not survive modern levels of scrutiny (11). Records from Morocco  mainly Nov–Mar, but first birds typically arrived late Aug/early Sept (exceptionally late Jul), with last departing as late as mid May (12); formerly irregular migrant in NE Africa late Jul to Aug and Apr–May. Status in Turkey uncertain, as some records of N. arquata orientalis have been erroneously attributed to present species, while other records never listed as definite were subsequently treated (erroneously) as such (13); six skins exist of birds shot in Istanbul area between mid 19th and perhaps early 20th century (14, 15). Status in Azerbaijan also uncertain; definite record of bird shot in Aug 1988, and species said to pass through regularly in very small numbers, but no documented records anywhere in C Asia since 1980 and several older records have recently re-evaluated and deemed unacceptable, especially from Kazakhstan (16). Vagrants recorded astonishingly wildly, as far afield as the Azores (Mar 1979, Jan 1981) (17), Canada (c. 1925) and Japan (in or prior to 1913, on Honshu) (18), but some such records have proven to be erroneous (e.g. in Czech Republic (19, 20), Myanmar (21), Seychelles (22) ) and others are unconfirmed (Djibouti (11), L Chad basin) (23).

Diet and Foraging

Outside breeding season, takes annelids, molluscs, snails, crustaceans and small insects, such as grasshoppers, earwigs and beetles. Probes in soft mud and soil or pecks from surface; observed taking insects from scrubby bushes. In winter, in Morocco, birds fed for 2–4 hours after dawn, then roosted at a lagoon, before feedingagain from mid-afternoon until near dusk, when they again roosted in the lagoon.

Sounds and Vocal Behavior

Very limited data. Gives a “cour-lee” similar to the call of N. arquata, but has been considered higher-pitched, shorter and more repeated, and sometimes followed by 5–7 very short “ti-ti-ti...” notes, which sounds like a laughing trill. The only known sound recording (flight call of a male  ) matches this description. A sweet, high-pitched and monosyllabic “kwee” has been heard from birds either taking off or landing (perhaps in alarm?). Also described is a hollow vibrating whistle (“sirrr-virrr”) or loud, high-pitched “be-be-be-be...”, given when the birds mobbed intruders on breeding territories (3).

Breeding

Very little known. Eggs found in May and species was said to arrive on breeding grounds no earlier than c. 10 May (3); may apparently breed in small colonies, with nests 2–3 m apart, up to 10–15 m apart; nest in dense growth on dry areas within bogs, constructed of dry grass and sited in shallow hollows. Four eggs (variation unknown), colour dark olive or yellowish green, with even dark brown or red-brown markings (3, 24), size variously reported as c. 52·5–54·5 mm × 38–40·1 mm and 64–65·6 mm × 45–47·1 mm (3). Few other data, but young said to fledge in early Jul and species was thought to depart breeding grounds in second half of Aug (3).

CRITICALLY ENDANGERED. CITES I. Has only been definitely recorded breeding in Tara region N of Omsk in SW Siberia (although also claimed in Iran), but no nesting records since 1925 and species was known to have been already declining around Omsk by first decade of 20th century (3). Until early 1890s probably very abundant on wintering areas in Morocco, Algeria and Tunisia, but since then numbers have declined dramatically and species is seriously threatened. Only regularly used wintering site was Merja Zerga , NW Morocco, but none recorded there since 1995 (perhaps 1998), while only recent claim from W Siberia involved a bird seen only in flight in Jul 1996 (3). In 1964, as many as 500–800 birds were counted in SW Morocco (12). During 1980–1990, there were only 103 records globally, involving 316–326 birds BirdLife International (2015) Species factsheet: Numenius tenuirostris. Downloaded from http://www.birdlife.org on 16/01/2015. , in 1990–1999, declining to 74 records involving 148–152 birds BirdLife International (2015) Species factsheet: Numenius tenuirostris. Downloaded from http://www.birdlife.org on 16/01/2015. . Between 1980 and 1995, some 25% of observations on record were made in Greece, of which 80% were at two localities (Evros Delta and Porto Lagos) (25), but it has been suggested that at least some of these records should be critically reassessed, given the lack of photo-documentation for many of these sightings and the paucity of records in the same period elsewhere within the species’ known range involving huge flocks as in Greece (11). Timeline to extinction may therefore have been much earlier than usually envisaged (the species was only admitted to list of globally threatened birds in 1980s). Although there have been reports from Bulgaria, Ukraine and Uzbekistan of larger groups, almost all recent sightings in entire non-breeding range usually involve only 1–5 birds; in S Italy, c. 20 birds reported in Jan–Mar 1995 (26); surprising report of 50 birds from Iran in 1994, but these not now generally accepted (see Movements). Last nationally accepted record is from Hungary in Apr 2001 (27), but British record from May 1998, originally accepted, now rejected (28, 29, 30, 31). Population estimated at 50–270 birds in 1994, but the extreme paucity of recent confirmed records suggests it is now fewer than 50 birds BirdLife International (2015) Species factsheet: Numenius tenuirostris. Downloaded from http://www.birdlife.org on 16/01/2015. and there has been intense speculation that species is already extinct (32). A Slender-billed Curlew Working Group was established in 1997 and relaunched in Dec 2008; its principal aim is to locate any surviving individuals, protect them and their habitats and, if a bird is found, to fit it with a satellite transmitter, in an effort to rediscover the species’ breeding grounds (10, 33). However, targeted surveys (e.g. in Iran (34), Kazakhstan (32), Saudi Arabia (35), Tunisia) (36), organized by the Working Group, have all failed to find any evidence for its survival. Species used to stage in steppes, and its decline may be due to massive loss of this particular habitat; also hunting, particularly on migration, and drainage of staging areas may have been significant. Breakdown of social behaviour patterns in a species that formerly migrated in large flocks may also constrain recovery. It has recently been suggested that the main breeding areas were not located in W Siberia but in steppe zone, which has been cultivated on a large scale, thus perhaps explaining rapid decline of species. Area N of Caspian Sea, between R Volga and R Ural, has been suggested as potential breeding location.

Distribution of the Slender-billed Curlew - Range Map
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  • Year-round
  • Migration
  • Breeding
  • Non-Breeding
Distribution of the Slender-billed Curlew

Recommended Citation

Van Gils, J., P. Wiersma, G. M. Kirwan, and C. J. Sharpe (2020). Slender-billed Curlew (Numenius tenuirostris), version 1.0. In Birds of the World (J. del Hoyo, A. Elliott, J. Sargatal, D. A. Christie, and E. de Juana, Editors). Cornell Lab of Ornithology, Ithaca, NY, USA. https://doi.org/10.2173/bow.slbcur.01
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