Numenius tenuirostris


Taxonomy [top]

Kingdom Phylum Class Order Family

Scientific Name: Numenius tenuirostris
Species Authority: Vieillot, 1817
Common Name(s):
English Slender-billed Curlew
French Courlis à bec grèle
Spanish Zarapito Fino

Assessment Information [top]

Red List Category & Criteria: Critically Endangered C2a(i,ii);D ver 3.1
Year Published: 2012
Date Assessed: 2012-05-01
Assessor(s): BirdLife International
Reviewer(s): Symes, A. & Butchart, S.
Contributor(s): Buchanan, G., Cleeves, T., Crockford, N., Gallo-Orsi, U., Hilton, G. & Smith, K.
Facilitator/Compiler(s): Benstead, P., Bird, J., Calvert, R., Derhé, M., Peet, N., Pilgrim, J., Symes, A.
There are very few recent confirmed records of this species and sightings have become more and more infrequent, presumably as a result of declines caused by habitat loss and exploitation. No regular breeding, passage or wintering population is known, and the number of remaining individuals must be tiny. For these reasons the species qualifies as Critically Endangered.

Geographic Range [top]

Range Description: Numenius tenuirostris has only been confirmed breeding near Tara, north of Omsk in Siberia, Russia, between 1909-1925. It migrates west-south-west from its presumed breeding grounds in Siberia through central and eastern Europe, predominantly Russia, Kazakhstan, Ukraine, Bulgaria, Hungary, Romania and the former Yugoslavia to southern Europe, Greece, Italy, and Turkey, and North Africa, Algeria, Morocco and Tunisia. It has also been reported from Slovenia, Uzbekistan, Turkmenistan, Saudi Arabia, and Yemen. Reports of birds staging in Ukraine persist but require confirmation. Regarded as very common in the early 19th century, it was already a rare bird by the 20th century, with regular records having dried up by the end of the century. Between 1980 and 1990, there were only 103 records involving 316-326 birds (BirdLife International 1999), and from 1990-1999, this dropped to 74 records involving 148-152 birds (BirdLife International 1999). Although there have been reports from Bulgaria, Ukraine and Uzbekistan of larger groups, most recent verified records have been of one to three birds, with the last nationally accepted record coming from Hungary in April 2001 (G. Buchanan & N. Crockford in litt. 2009; Oláh and Pigniczki 2010). In 1994, the population was estimated at only 50-270 individuals, but the paucity of recent confirmed records suggests it may now be lower than 50 birds.

Albania; Algeria; Azerbaijan; Bulgaria; Croatia; Greece; Hungary; Iran, Islamic Republic of; Iraq; Italy; Kazakhstan; Macedonia, the former Yugoslav Republic of; Montenegro; Morocco; Romania; Russian Federation; Saudi Arabia; Serbia (Serbia); Tunisia; Turkey; Ukraine; Uzbekistan; Yemen
Austria; Bosnia and Herzegovina; Canada; Cyprus; Egypt; France; Germany; Israel; Kuwait; Malta; Netherlands; Palestinian Territory, Occupied; Poland; Portugal; Spain; Switzerland; United Kingdom
Present - origin uncertain:
Czech Republic; Japan; Libya
Range Map: Click here to open the map viewer and explore range.

Population [top]

Population: The population is assumed to be tiny (fewer than 50 individuals and mature individuals) based on small number of recent records, most of which are of just 1-3 individuals.
For further information about this species, see 22693185_numenius_tenuirostris.pdf.
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Population Trend: Decreasing

Habitat and Ecology [top]

Habitat and Ecology: Behaviour This species is migratory (del Hoyo et al. 1996). It is thought to breed in small colonies with nests between 2-3 m and 10-15 m apart (del Hoyo et al. 1996). Eggs have been found in May (del Hoyo et al. 1996). Early records often referred to the species as occurring in large flocks on migration and in winter. However, it is some decades since any sizeable flocks have been observed. The peak of the autumn migration appears to occur around September, with the spring migration peaking around March (Gretton 1991). Habitat Breeding The only known nests were recorded in bog-forest transition zones (Gretton 1991) on the northern limit of the forest-steppe zone in habitat more typical of taiga marsh. This may represent either a very specialised breeding habitat requirement, or an unusual use of habitat at the limit of the species's breeding range (Gretton 1991). Non-breeding On migration and in winter, a wide variety of habitats are used, including saltmarsh, steppe grassland, fishponds, saltpans, brackish lagoons, tidal mudflats, semi-desert, brackish wetlands and sandy farmland next to lagoons. Large coastal wetland complexes may be especially characteristic, and most records come from close to the sea (Buchanan et al. 2010). Where it winters inland it inhabits marsh areas fed with freshwater, but with areas of Salicornia indicating that the ground has a high salt content (Gretton 1991). Diet There is little information on its diet: birds at Merja Zerga (Morocco) fed on earthworms and tipulid larvae, while elsewhere insects (there is a suspiscion that orthoptera may have been an important food source [N. Crockford in litt. 2012]), molluscs and crustaceans have been recorded as prey. Breeding site The nest found by Ushakov in 1914 was constructed of dry grass with a few leaves of rush Scirpus but little or no sedge (Gretton 1991). The known nests were situated on dry areas of sedge and bog moss some distance from willow scrub or birch grove (Gretton 1991).

Systems: Terrestrial; Freshwater; Marine

Threats [top]

Major Threat(s): Threats on the breeding grounds are unknown. Within its potential breeding range, the taiga has been little modified, the forest-steppe partially cultivated and much of the steppe modified by agriculture. Habitat loss in the wintering grounds is of unknown importance. There has been extensive drainage of wetlands in the Mediterranean and North Africa and potentially important areas in Iraq. The conversion of European wetlands and central European steppes to arable farmland may have heavily impacted the species in depriving it of important habitats during migration (Gretton 1991). Historically hunting was high, and may have been the key factor in its decline. Following the initial decline, breakdown of social behaviour patterns may have prevented recovery. Historically a gregarious species, smaller groups or individuals may have difficulty in locating suitable stop-over sites on migration (Gretton 1991). Individuals may join flocks of N. arquata, being led to unsuitable wintering habitat and rendered unlikely to find a mate (Gretton 1991).

Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
CITES Appendix I. CMS Appendix I and II. A Memorandum of Understanding, established under the auspices of the CMS, came into effect in 1994, and a working group was established in 1998 (Gallo-Orsi and Boere 2001). An international action plan was published in 1996. National action plans are in place in Italy (Nagy and Crockford 2004), Bulgaria and Ukraine. Several of the sites within the EU where the species has been recorded are designated as Special Protection Areas. There have been several international initiatives to survey passage and wintering sites (Azafzaf and Feltrup-Azafzaf 2003; T. R. Cleeves in litt. 2006; van der Have et al. 2001) and potential breeding areas (Gallo-Orsi and Boere 2001; Gretton et al. 2002), collate records (Gallo-Orsi and Boere 2001), protect key sites, raise public awareness (Azafzaf and Feltrup-Azafzaf 2003) and educate hunters. Details of a 'last push' to locate any remaining populations (focusing initially on surveys of historical wintering areas) were announced at the Ninth Meeting of the Conference of the Parties to the Convention on Migratory Species in December 2008 (BirdLife International 2008; RSPB 2010; Crockford 2009). Surveys across the potential non-breeding range (from Morocco, perhaps as far as Japan) took place in 2009-11 with a particular focus on wintering and potential moult sites (G. Buchanan & N. Crockford in litt. 2012). The Slender-billed Curlew Working Group has developed a tool kit to assist people to identify and report Slender-billed Curlew in the field (available at: If any can be found and caught then the sites used during the annual cycle could be determined by satellite tagging. An attempt to narrow down the search for breeding and moulting sites using stable isotope analysis and Strontium analysis of museum skins commenced in 2002 (Hilton 2003); preliminary results suggest that the main breeding area may have extended from southern central Russia into northern Kazakhstan (Nagy and Crockford 2004; G. Buchanan & N. Crockford in litt. 2012).

Conservation Actions Proposed
Continue to monitor key former and potential wintering and passage sites. Search for breeding grounds (taking into account results of stable isotope analysis). Attach satellite transmitters to captured birds. Provide training in species identification along the migration route. Promote protection of habitat. Provide legal protection for this and similar species. Increase public awareness.

Citation: BirdLife International 2012. Numenius tenuirostris. The IUCN Red List of Threatened Species. Version 2015.2. <>. Downloaded on 31 August 2015.
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