Numenius madagascariensis 


Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Charadriiformes Scolopacidae

Scientific Name: Numenius madagascariensis
Species Authority: (Linnaeus, 1766)
Common Name(s):
English Far Eastern Curlew, Eastern Curlew
Taxonomic Source(s): del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Lynx Edicions BirdLife International.
Taxonomic Notes:

Identification information: 63 cm. Largest wader in New Zealand. Greyish brown and buff streaked body; very long downcurved bill (19 cm). Similar spp. Distinguished from other similar species by large size and very long bill. Voice Flight call 'croo-lee'.

Assessment Information [top]

Red List Category & Criteria: Endangered A2bc+3bc+4bc ver 3.1
Year Published: 2015
Date Assessed: 2015-10-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S.
Contributor(s): Amano, H., Moores, N., Rogers, D. & Crockford, N.
Facilitator/Compiler(s): Benstead, P., Butchart, S., Calvert, R., Derhé, M., Ekstrom, J., Harding, M., Symes, A. & Ashpole, J
This species has been uplisted to Endangered as new information suggests it is undergoing a very rapid population decline which is suspected to have been primarily driven by habitat loss and deterioration in the Yellow Sea region. Further proposed reclamation projects are predicted to cause additional declines in the future

Previously published Red List assessments:
2012 Vulnerable (VU)
2010 Vulnerable (VU)
2009 Least Concern (LC)
2008 Least Concern (LC)
2004 Least Concern (LC)
2000 Lower Risk/near threatened (LR/nt)
1994 Lower Risk/near threatened (LR/nt)
1988 Lower Risk/least concern (LR/lc)

Geographic Range [top]

Range Description: This species breeds in eastern Russia, from the upper reaches of the Nizhnyaya Tunguska river east though the Verkhoyarsk mountains to Kamchatka, and south to Primorye and north-eastern Mongolia (del Hoyo et al. 1996). The Yellow Sea of North Korea, South Korea and China is a particularly important stopover site on migration. It has been recorded as a passage migrant in Japan, Brunei, Bangladesh, Thailand, Viet Nam, Philippines, Malaysia and Singapore, with most birds wintering in Australia, but also in China, Indonesia, Papua New Guinea, and New Zealand (del Hoyo et al. 1996). The global population has recently been estimated at 32,000 individuals (Wetlands International 2015), including 28,000 in Australia (Bamford et al. 2008). The global population is declining, as indicated by reduced numbers at stopover points in South Korea and Japan, and a rapid decline in the number of non-breeding individuals wintering around Australia and New Zealand (Amano 2006, Gosbell and Clemens 2006, Moores et al. in litt. 2008, D. Rogers et al. in litt. 2009, Wilson et al. 2011, Studds et al. in prep.).

Countries occurrence:
Australia; Brunei Darussalam; China; Fiji; Guam; Hong Kong; Indonesia; Japan; Korea, Democratic People's Republic of; Korea, Republic of; Malaysia; Micronesia, Federated States of ; Mongolia; New Zealand; Northern Mariana Islands; Palau; Papua New Guinea; Philippines; Russian Federation; Singapore; Taiwan, Province of China; Thailand; Timor-Leste; Viet Nam
Bangladesh; Iran, Islamic Republic of; Oman; United States
Present - origin uncertain:
Continuing decline in area of occupancy (AOO): Yes
Extreme fluctuations in area of occupancy (AOO): No
Estimated extent of occurrence (EOO) - km2: 727000
Continuing decline in extent of occurrence (EOO): Unknown
Extreme fluctuations in extent of occurrence (EOO): No
Continuing decline in number of locations: Yes
Extreme fluctuations in the number of locations: No
Range Map: Click here to open the map viewer and explore range.

Population [top]

Population: Wetlands International (2006) estimated the global population at c. 38,000 individuals, although a more recent update now estimates the population at 32,000 individuals (Wetlands International 2015). It is therefore placed in the band 20,000-49,999 individuals.

Trend Justification:  An analysis of monitoring data collected from around Australia and New Zealand (Studds et al. in prep.) suggests that the species has declined much more rapidly than was previously thought; with an annual rate of decline of 0.058 equating to a loss of 81.7% over three generations. Loss of habitat at critical stopover sites in the Yellow Sea is suspected to be the key threat to this species and given that it is restricted to the East Asian-Australasian Flyway, the declines in the non-breeding population are thought to be representative of the global population.

Local-scale declines have also been reported: the species has been declining steadily in Australia, at a rate of 2.4% annually in Moreton Bay between 1992 and 2008 (Wilson et al. 2011);  c. 5% annually in Victoria between 1980 and 2010 (D. Rogers in litt. 2012); by over 65% in Tasmania since the 1950s (Reid and Park 2003); and by 40% across 49 Australian sites between c. 1983 and c. 2007 (D. Rogers et al. in litt. 2009, Birds Australia in litt. to Garnett et al. 2011). Declines seem equally worrying in North-western Australia (D. Rogers in litt. 2012). Furthermore, the population at Saemangeum (South Korea) has decreased by 32.6% (c. 1,800 birds) between 2006 and 2008 due to the reclamation of tidal flats (Moores 2006, Moores et al. in litt. 2008). Although these sites only represent a proportion of the wintering and stopover populations, threats are widespread and are projected to cause population declines in the future (D. Rogers in litt. 2009). Given that more reclamation is proposed within the Yellow Sea,with widespread threats elsewhere on the flyway, it is assumed that these declines will continue.

Current Population Trend: Decreasing
Additional data:
Continuing decline of mature individuals: Yes
Extreme fluctuations: No Population severely fragmented: No
Continuing decline in subpopulations: Unknown
Extreme fluctuations in subpopulations: No All individuals in one subpopulation: No

Habitat and Ecology [top]

Habitat and Ecology: The species breeds on open mossy or transitional bogs, moss-lichen bogs and wet meadows, and on the swampy shores of small lakes; in the non-breeding season it is essentially coastal, occurring at estuaries, mangrove swamps, saltmarshes and intertidal flats, particularly those with extensive seagrass (Zosteraceae) meadows. It often roosts in salt-marshes, behind mangroves, or on sandy beaches (del Hoyo et al. 1996). Its diet on breeding grounds includes insects, such as larvae of beetles and flies, and amphipods. Berries are also consumed during the autumn migration. In non-breeding areas it feeds on marine invertebrates, preferentially taking crabs and small molluscs but also feeding on other crustaceans and polychaete worms (del Hoyo et al. 1996). This migratory wader nests from early May to late June, often in small colonies of 2-3 pairs, with an average clutch size of four eggs. It probably delays maturity longer than most shorebirds, perhaps not breeding until 3-4 years old (del Hoyo et al. 1996, Rogers 2006).

Systems: Terrestrial; Freshwater; Marine
Continuing decline in area, extent and/or quality of habitat: Yes
Generation Length (years): 10.1
Movement patterns: Full Migrant
Congregatory: Congregatory (and dispersive)

Threats [top]

Major Threat(s): Habitat loss on the Yellow Sea staging grounds is probably the primary threat to the species, with loss of stopover sites thought to be responsible for shorebird population declines on the East Asian-Australasian Flyway (Amano et al. 2010, Yang et al. 2011). It is estimated that up to 65% of intertidal habitat in the Yellow Sea has been lost over the past 50 years, with the rate of habitat loss estimated at >1% every year (Murray et al. 2014). This scale of habitat loss is predicted to continue owing to growing populations around the Yellow Sea. It is difficult to ascertain whether declines seen at reclaimed sites such as Saemangeum represent true declines, or whether the birds have simply been displaced (Moores et al. in litt. 2008, D. Rogers in litt. 2009), but the former seems more probable, given the huge scale of habitat loss in the Yellow Sea. Wetland degradation in the Yellow Sea may affect the species where it stages on migration (Bamford et al. 2008, van de Kam et al. 2010). Further threats may include disturbance at the nesting and feeding sites, direct persecution throughout its range, and a decrease in the availability of food due to pollution at stopover points in South Korea. Furthermore, females probably tend to migrate further south to southern Australian wetlands which are more threatened than those in northern Australia (del Hoyo et al. 1996).

Conservation Actions [top]

Conservation Actions: Conservation and Research Actions Underway
CMS Appendix I. The species was accepted as a Concerted Action species under CMS in November 2014 (Anon. 2014). Population trends are being monitored in Australia as part of the Monitoring Yellow Sea Migrants in Australia project. The species is included in the action plan for Australian birds 2010 (Garnett et al. 2011) and was recently uplisted to Critically Endangered in Australia.

Conservation a
nd Research Actions ProposedIdentify key stopover areas and prevent their reclamation. Continue to monitor population trends. Restore reclaimed wetland sites. Campaign to stop shorebird hunting in Asian countries. Legally protect it in all range states. Survey the breeding grounds for potential threats. The proposal for listing as a species for Concerted Action under CMS stated that conservation actions were needed to: 1) Protect staging habitat and manage habitat in the Yellow River Delta and remaining habitat at Yala Jiang and other sites in the Yellow Sea; 2) Manage shellfisheries at key sites to benefit the species (Leyrer et al. 2014).

Citation: BirdLife International. 2015. Numenius madagascariensis. The IUCN Red List of Threatened Species 2015: e.T22693199A67194768. . Downloaded on 29 November 2015.
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