Species names in all available languages
| Language | Common name |
|---|---|
| Afrikaans | Lepelbekstrandloper |
| Bangla (India) | ঘুড়ঘুড়ি |
| Basque | Txirri mokozabala |
| Bulgarian | Чукотски брегобегач |
| Catalan | territ becplaner |
| Chinese | 琵嘴鷸 |
| Chinese (Hong Kong SAR China) | 勺嘴鷸 |
| Chinese (SIM) | 勺嘴鹬 |
| Croatian | žalar žličar |
| Czech | jespák lžícozobý |
| Danish | Skeryle |
| Dutch | Lepelbekstrandloper |
| English | Spoon-billed Sandpiper |
| English (AVI) | Spoon-billed Sandpiper |
| English (United States) | Spoon-billed Sandpiper |
| Estonian | luitsnokk-rüdi |
| Finnish | lusikkasirri |
| French | Bécasseau spatule |
| French (Canada) | Bécasseau spatule |
| German | Löffelstrandläufer |
| Hebrew | חופית כפנית |
| Hungarian | Kanálcsűrű parfutó |
| Icelandic | Skeiðtíta |
| Indonesian | Kedidi paruh-sendok |
| Japanese | ヘラシギ |
| Korean | 넓적부리도요 |
| Norwegian | skjesnipe |
| Polish | biegus łyżkodzioby |
| Russian | Лопатень |
| Serbian | Sprutka kašikara |
| Slovak | pobrežník lopatkozobý |
| Slovenian | Žličasti prodnik |
| Spanish | Correlimos Cuchareta |
| Spanish (Spain) | Correlimos cuchareta |
| Swedish | skedsnäppa |
| Thai | นกชายเลนปากช้อน |
| Turkish | Kaşık Gagalı Kumkuşu |
| Ukrainian | Лопатень |
Revision Notes
Sayam U. Chowdhury and Christoph Zöckler revised the account. Peter Pyle made contributions to the Plumages, Molts, and Structure page, and Peter F. D. Boesman made contributions to the Sounds and Vocal Behavior page.
Calidris pygmaea (Linnaeus, 1758)
Definitions
- CALIDRIS
- calidris
- pygmaea / pygmaeum / pygmaeus / pygmea / pygmeum / pygmeus
The Key to Scientific Names
Legend Overview
Spoon-billed Sandpiper Calidris pygmaea Scientific name definitions
Version: 2.0 — Published May 5, 2025
Conservation and Management
Conservation Status
CRITICALLY ENDANGERED. One of the most charismatic of the world’s endangered bird species, it has attracted considerable attention since its plight became apparent (61). It has a very small population that is declining extremely rapidly (see Demography and Populations: Population Status), the realization of which (61) caused its uplisting from Vulnerable to Endangered in 2004, and to Critically Endangered in 2008 (BirdLife). It has probably always been fairly scarce due to its small range, restricted to a narrow coastal zone, combined with very specialized breeding habitat requirements, and although it has a relatively large wintering range, it occurs regularly at only a few sites (BirdLife). The most important sites are currently estimated to be the Gulf of Mottama (Martaban, a Ramsar site) and Nan Thar, Myanmar, and Sonadia Island, Bangladesh (69), although there is also evidence that a significant proportion of the remaining population is wintering in southwestern Guangdong (southern China) (73, 1).
All of the available evidence indicates that the breeding range has contracted in recent decades (69). Declines have occurred at all known breeding sites and it is unlikely that significant colonies remain to be discovered (BirdLife). The main threat appears to be habitat loss along the migration route (especially Korea and China) and in wintering areas (74, 33, BirdLife), where tidal flats are being reclaimed for industry, infrastructure and aquaculture, and are becoming increasingly polluted, while other potentially threatening habitat changes have been reported at sites in eastern India (75) and Bangladesh (48). Hunting and accidental trapping continues to threaten the species across its nonbreeding range (76, 64, 77, 65). Other threats on breeding grounds include hunting and collection of birds by specimen collectors (33).
Effects of Human Activity
Habitat Loss and Degradation
Human activities pose significant threats to the Spoon-billed Sandpiper throughout its migratory and wintering ranges. The most pressing threat is the reclamation of tidal flats for coastal development, including industries, leisure facilities, infrastructure, aquaculture, and agriculture. These developments are particularly destructive to the intertidal mudflats that the species depends on during migration and wintering.
The reclamation of the Saemangeum and Geum estuaries in South Korea, which once served as important staging areas for thousands of migratory shorebirds, has drastically reduced the presence of Spoon-billed Sandpiper in the region. Since the completion of the Saemangeum reclamation in 2007, only a single individual has been recorded annually, compared to the hundreds that were observed before the development (78).
Other key sites, such as the Tiaozini wetlands within the Rudong mudflats in China, have also faced threats from large-scale reclamation projects. Plans for reclaiming over 60,000 hectares of mudflats by 2020 were expected to significantly impact this critical habitat (74, 52). Fortunately, a national announcement in January 2018 put an end to further reclamation of intertidal lands in China, and these sites have been nominated for World Heritage status (29). Nevertheless, ongoing development, including new seawall constructions at Rudong, continues to pose a threat to the mudflats (52).
Effects of Invasive Species
Invasive species like smooth cordgrass (Spartina alterniflora [= Sporobolus alterniflorus]), introduced to stabilize mudflats for reclamation projects, have also significantly reduced the availability of suitable habitats for Spoon-billed Sandpiper. This invasive grass has spread rapidly across key sites, including Rudong and Dongling, forming dense stands that make the intertidal areas unsuitable for foraging (52).
Hunting and Trapping
Hunting poses a critical threat to Spoon-billed Sandpiper, particularly in Bangladesh, China, Vietnam, and Myanmar, where they are frequently caught in nets intended for larger waders. Although not specifically targeted, the accidental capture of Spoon-billed Sandpiper in mist nets has contributed to a decline in their numbers (65, 35, 29). Hunting is especially detrimental to juvenile birds, which remain in non-breeding areas for up to two years, increasing their exposure to capture (33). However, recent conservation efforts aimed at reducing trapping on the wintering grounds have been successful in some regions, particularly in Bangladesh and Myanmar (65, 36).
Accidental bycatch in fishing nets is another major concern, particularly in China, where monofilament nets are set over high tides in key migratory areas. In 2015, multiple birds, including one juvenile Spoon-billed Sandpiper, were found trapped in nets at Tiaozini during a single nocturnal high tide (52). Although conservation efforts have reduced the use of illegal mist nets in some areas, such as south-west Guangdong Province, hunting and netting continue to threaten the species across parts of its range (65, 29).
Pesticides and Other Contaminants/Toxics
Diseases and pollution may also contribute to mortality among the adult birds. However, little data are available to substantiate a direct link between high levels of heavy metals and polychlorinated biphenyls (PCB) or other pollutants and the mortality of Spoon-billed Sandpiper. In 2014, a large number of waterbirds and other migratory species were found dead at a key staging areas in the Jiangsu Province near Rudong including at least two Spoon-billed Sandpiper. While pollution or avian disease may have caused this abrupt mortality during migration, the exact reason could not be determined (29).
Collisions with Stationary/Moving Structures or Objects
The Rudong mudflats are home to Asia’s largest wind farm, which presents a potential risk to the species during migration.
Human/Research Impacts
On the breeding grounds, human activity poses fewer immediate threats, but local disturbances such as nest destruction by dogs and human encroachment have been recorded near villages (79). Nest predation by foxes and skuas, combined with poor weather conditions, has further reduced breeding productivity (62,27).
Climate Change
Climate change is expected to have a profound impact on the species, as rising temperatures and shifting tundra ecosystems alter the species’ breeding habitat. Recent observations indicate that expanding bushes are encroaching on the southern tundra breeding grounds, while drying conditions in the northern range may limit access to food for breeding waders (29).
Management
Conservation Areas
Information needed.
Conservation Measures and Habitat Measurement
A consortium of organizations in Europe and Asia is now involved in research and conservation activities, especially in Russia, where main breeding areas are closely monitored each breeding season and many birds individually marked, to permit identification on passage and in winter without retrapping (41). There is some evidence that work to eliminate, or at least reduce, trapping of shorebirds, among them this species, on the wintering grounds is starting to have effect (80), with considerable efforts being made to raise the awareness of local peoples to its plight (69).
A captive-rearing and breeding program commenced in 2011, with eggs collected in Chukotka, Russia, and young reared at Wildfowl and Wetlands Trust facilities in the UK (29). In October 2024, the captive population numbered only two birds. In addition, since 2012, eggs are being hatched and young raised in captivity close to the breeding sites, and then released to migrate south with wild-bred juveniles – this intervention is popularly known as headstarting (60, 81, 49).