This species has been uplisted to Near Threatened because it is estimated to have undergone a moderately rapid decline over the past three generations (22 years). Over-exploitation in the non-breeding range (in particular in Suriname) may be the principal driver of declines, with eastern-breeding populations also potentially declining due to reduced food supply at key staging sites, but further information on the rate and drivers of declines is needed.
Distribution and populationCalidris pusilla
AERC TAC. 2003. AERC TAC Checklist of bird taxa occurring in Western Palearctic region, 15th Draft. Available at: #http://www.aerc.eu/DOCS/Bird_taxa_of _the_WP15.xls#.
Cramp, S.; Perrins, C. M. 1977-1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. Oxford University Press, Oxford.
del Hoyo, J.; Collar, N. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.
SACC. 2006. A classification of the bird species of South America. Available at: #http://www.museum.lsu.edu/~Remsen/SACCBaseline.html#.
is a common breeder in the Arctic and subarctic from far-eastern Siberia (Russia
) east across Alaska (USA
) and northern Canada
to Baffin Island and Labrador (Chandler 2009). In the non-breeding season the species uses coastal estuarine habitats, wintering on the Pacific coast from Mexico
, and on the Atlantic coast from the Yucatan and the West Indies south to central Argentina
, with large non-breeding concentrations occurring along the coast of Suriname
and French Guiana
(del Hoyo et al.
1996, Chandler 2009, D. Mizrahi in litt.
2009). The population was formerly estimated at 3.5 million individuals, but this was revised downwards to 2.2 million individuals in 2006 (Morrison et al.
2006, A. Lesterhuis in litt.
2009) assuming annual declines of 5% in 75% of the North American population. Trends are hard to quantify, but aerial surveys conducted along the coasts of Suriname and French Guiana suggest that the non-breeding population in the region could have declined by c.80% between the early 1980s and 2008, from c.2 million to c.400,000 individuals; the possibility that there has been a shift in the wintering range seems unlikely but has not been completely ruled out (D. Mizrahi in litt.
The population was formerly estimated at 3.5 million individuals, but this was revised downwards to 2.2 million individuals in 2006 (Morrison et al.
2006, A. Lesterhuis in litt.
2009) assuming annual declines of 5% in 75% of the North American population.Trend justification
This species is conservatively estimated to have declined at a rate approaching 30% over three generations (22 years). Determining the exact population trajectory is very difficult, but aerial surveys along the coasts of Suriname, French Guiana and Guyana (which may support c.85% of the population wintering on the coast of South America) suggest that the non-breeding population may have declined by c.79% between the early 1980s and 2008 (Morrison et al.
2012), while data from the Bay of Fundy show a 68% decline during southbound migration between 1982 and 2005, with the greatest reductions taking place since the mid 1990s. Preliminary results from surveys of the Brazilian coast (Belem to Baia de Sanadi) in 2011 suggest that declines have also taken place here since 1982, making it unlikely that a southward shift in wintering range accounts for the declines in Suriname and French Guiana (D. Mizrahi in litt.
2011). Long-term population trend indices also suggest that Semipalmated Sandpiper has declined significantly since the 1980s, especially populations migrating along the Atlantic Coast en route to eastern Canadian breeding areas (Mizrahi et al.
2012). However, data from the breeding range suggests that the species was generally increasing or stable in the western and central portions of the range and had an uncertain status in the east (Smith et al.
2012), making the overall picture difficult to determine.Ecology
It breeds in high and low Arctic and subarctic wet sedge or heath tundra, oftern near pools, rivers and lakes (del Hoyo et al.
1996). In the non-breeding season it is mainly coastal, favouring sandy beaches and intertidal mudflats, sometimes also shallow lagoons and saltmarsh (del Hoyo et al.
1996). On migration also at inland wetlands, lake edges etc (del Hoyo et al.
1996). Food is mainly chironomid larvae in the breeding season, along with other small invertebrates and seeds. Various small aquatic, marine and terrestrial invertebrates taken on migration, including horseshoe crab Limulus polyphemus
eggs on spring migration in eastern USA (del Hoyo et al.
1996). Makes non-stop flights of up to 4,000 km on migration, with flocks of up to 350,000 gathering at key stopover sites (del Hoyo et al.
Hunting of shorebirds in northern South America, which is legal in French Guiana but illegal in Suriname, is widespread and thus a potential threat to C. pusilla
. Shorebirds killed by hunters in Suriname are estimated to number several tens of thousands annually, involving mainly C. pusilla
and Tringa flavipes
: if 20,000 C. pusilla
were removed from a population of two million annually (1% decrease, net after recruitment), the decline would amount to some 26% over 30 years, independent of other mortality, suggesting hunting could be a significant factor in the observed declines (Morrison et al.
2012). Poaching in Suriname may have increased over the last c.20 years owing to improvements in weaponry and transportation. Another potential threat is the harvesting of horseshoe crabs Limulus polyphemus
in Delaware Bay, an area which reportedly sees the passage of c.60% of the total population of C. pusilla
during the spring migration. The species feeds primarily on horseshoe crab
eggs during episodes of rapid mass accumulation, but harvest pressure from 1995-2005 dramatically reduced egg availability (Mizrahi et al.
2012). Significant changes in the intertidal profile, for unknown reasons, have taken place along the coast of the Guianas, although numbers of birds were also lower in areas with no obvious changes in mudflat area (Morrison et al.
2012). Use of pesticides in agricultural areas such as rice fields may affect shorebirds using those habitats directly, and drainage of pesticides into coastal areas and onto mudflats also has the potential to affect shorebirds (Morrison et al.
2012). Small-scale gold mining has increased considerably in the northern South American wintering range, and mercury, which is used in the extraction process and can reach the coast via the rivers, has the potential to affect shorebirds in coastal areas (Morrison et al.
2012). Oil exploration has also begun in Suriname and Guyana, with spills representing a further potential threat. Increasing frequency and severity of hurricanes during southbound migration may be causing increased mortality during this period (Morrison et al.
2012).Conservation Actions Underway
No species-specific actions are known. Hunting of shorebirds is illegal in Suriname, but this is poorly enforced. An adaptive management plan for Delaware Bay was formally adopted by the Atlantic States Marine Fisheries Commission in 2012. The plan links harvest decisions to information on the welfare of both horseshoe crab and Red Knot Calidris canutus
population levels as well as the use of crabs for bait and by the medical industry, and calls for crab harvest levels to be regularly adjusted in response to data on Red Knot and horseshoe crab populations.
Conservation Actions Proposed
Carry out systematic monitoring in breedng areas, key staging sites and wintering sites. Evaluate key threats, in particular mortality from hunting. Campaign for better enforcement of hunting regulations and the introduction of these where they do not currently exist. Support adaptive management plan for horseshoe crab harvest in Delaware Bay.
Related state of the world's birds case studies
Andres, B.A.; Gratto-Trevor, C.; Hicklin, P.; Mizrahi, D.; Morrison, R.I.G.; Smith, P.A. 2012. Status of the Semipalmated Sandpiper. Waterbirds 35(1): 146-148.
Butler, C. J. 2003. The disproportionate effect of global warming on the arrival dates of short-distance migratory birds in North America. Ibis 145: 484-495.
Chandler, R. 2009. Shorebirds of the Northern Hemisphere. Christopher Helm, London.
del Hoyo, J.; Elliott, A.; Sargatal, J. 1996. Handbook of the Birds of the World, vol. 3: Hoatzin to Auks. Lynx Edicions, Barcelona, Spain.
Delany, S.; Scott, D. 2006. Waterbird population estimates. Wetlands International, Wageningen, The Netherlands.
Mizrahi, D.; Peters, K.A.; Hodgetts, P.A. 2012. Energetic Condition of Semipalmated and Least Sandpipers during Northbound Migration Staging Periods in Delaware Bay. Waterbirds 35(1): 135-145.
Morrison, R. I. G.; McCaffery, B. J.; Gill, R. E.; Skagen, S. K.; Jones, S. L.; Page, G. W.; Gratto-Trevor, C. L.; Andres, B. A. 2006. Population estimates of North American shorebirds, 2006. Wader Study Group Bulletin: 67-85.
Morrison, R.I.G.; Mizrahi, D.S.; Ross, R.K.; Ottema, O.H.; de Pracontal, N.; Narine, A. 2012. Dramatic Declines of Semipalmated Sandpipers on their Major Wintering Areas in the Guianas, Northern South America. Waterbirds 35(1): 120-134.
Smith, P.A.; Gratto-Trevor, C.L.; Collins, B.T.; Fellows, S.D.; Lanctot, R.B.; Liebezeit, J.; McCaffery, B.J.; Tracy, D.; Rausch, J.; Kendall, S.; Zack, S.; Gates, H.R. 2012. Trends in Abundance of Semipalmated Sandpipers: Evidence from the Arctic. Waterbirds 35(1): 106-119.
Further web sources of information
Explore HBW Alive for further information on this species
Search for photos and videos, and hear sounds of this species from the Internet Bird Collection
Text account compilers
Butchart, S., Ekstrom, J., Symes, A.
Andres, B., Mizrahi, D., Brown, A., Lesterhuis, A.
IUCN Red List evaluators
Butchart, S., Taylor, J.
BirdLife International (2016) Species factsheet: Calidris pusilla. Downloaded from
http://www.birdlife.org on 24/08/2016.
Recommended citation for factsheets for more than one species: BirdLife International (2016) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 24/08/2016.
This information is based upon, and updates, the information published in BirdLife International (2000)
Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004)
Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.
To provide new information to update this factsheet or to correct any errors, please email BirdLife
To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.
Additional resources for this species