Taxonomic note
Calidris falcinellus (del Hoyo and Collar 2014) was previously placed in the genus Limicola.
Taxonomic source(s)
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.
Christidis, L. and Boles, W.E. 2008. Systematics and Taxonomy of Australian Birds. CSIRO Publishing, Collingwood, Australia.
Cramp, S. and Simmons, K.E.L. (eds). 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. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.
Turbott, E.G. 1990. Checklist of the Birds of New Zealand. Ornithological Society of New Zealand, Wellington.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | A2bc+4bc |
Year | Category | Criteria |
---|---|---|
2024 | Vulnerable | A2bc+4bc |
2016 | Least Concern | |
2012 | Least Concern | |
2009 | Least Concern | |
2008 | Least Concern | |
2004 | Least Concern | |
2000 | Lower Risk/Least Concern | |
1994 | Lower Risk/Least Concern | |
1988 | Lower Risk/Least Concern |
Migratory status | full migrant | Forest dependency | does not normally occur in forest |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 6,100,000 km2 | medium |
Extent of Occurrence (non-breeding) | 64,700,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 96000-136000 mature individuals | medium | estimated | 2023 |
Population trend | decreasing | - | inferred | 2014-2026 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Generation length | 4.36 years | - | - | - |
Number of subpopulations | 2 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: Divided into two subspecies, with the nominate breeding in Fennoscandia and north-west Russia, and sibirica breeding in central and eastern Siberia. Almost all of the nominate subspecies breeds in Europe, where there are estimated to be be 30,000-44,000 pairs, most of which (25,000-35,000 pairs) are in Finland (Keller et al. 2020). A much smaller number (<1,200 pairs) breed in European Russia (Keller et al. 2020). When immatures and non-breeding birds are taken into account, these numbers are similar to the wintering population of 61,000-110,000 birds estimated (BirdLife International 2021, Wetlands International 2023). Taxon sibirica is estimated to number 30,000 birds in the East Asian-Australasian Flyway (Mundkur and Langendoen 2022, Hansen et al. 2023); assuming approximately 0.6-0.8 birds are mature, this equates to c.18,000-24,000 breeding pairs. Overall, the global population of this species is estimated a 48,000-68,000 breeding pairs, or 96,000-136,000 mature individuals.
Trend justification: Few data are available from which to derive trends, but the sparse data that are indicate that this species is declining, potentially rapidly.
C. falcinellus is considered a difficult species to monitor because sample sizes observed in any given year are typically small. Based on analysis of breeding data from Finland, the species may have declined by 83% and 72% in the time periods 2006-2023 and 2009-2023 respectively; however these rates of reduction are thought to be too high, and to have overestimated the species' abundance in 2009-2011 (A. Lehikoinen in litt. 2024). An alternative analysis, using the same data, separating observations by decade and using a GLMM, suggested a more modest reduction of c.41% over 17 years (equivalent to fractionally more than 30% over three generations). While again based on small sample sizes, migration counts from Hanko Bird Observatory indicate both a long-term (1979-1999 to 2020-present) and short-term (2010-2019 to 2020-present) decline, although these are reportedly affected by weather conditions (A. Lehikoinen in litt. 2024). In Sweden, trends are also probably negative (a decrease of c.5% per year), but again sample sizes are small and the overall trend is statistically not significant (Svensk Fågeltaxering 2024). These declines mirror the breeding range contraction in Keller et al. (2020), particularly at the southern margin of the Finnish distribution, as well as in Sweden. Moreover, joint trend data from monitoring in Finland, Sweden and Norway also suggest a relatively rapid decline between 2006 and 2018 (Lindström et al. 2019), equivalent to 5.6% per year (or c.53% over three generations).
Trends in sibirica are broadly unknown. Data from Myanmar suggest declines of c.50% in recent years at one site that formerly hosted c.4,000 birds (but now reduced to a maximum of 2,100) (Aung et al. 2023) and numbers at other sites have reportedly also declined, but these host only small numbers (C. Zöckler in litt. 2024). No other data are known, but given C. f. falcinellus comprises c.2/3 of the global population, it is highly likely that the global population is declining at least a moderately rapid rate.
To account for various uncertainties in the data collected, C. falcinellus is estimated to have declined by 30-49% over the past three generations (13 years: 2011-2024), and this reduction is also likely to be true for the window 2014-2026, thus qualifying this species for Vulnerable under Criterion A4, as well as A2. Future rates of decline, however, are highly uncertain, and plausible rates of reduction are not estimated for over the next three generations.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Afghanistan | extant | native | yes | |||
Albania | extant | native | yes | |||
Algeria | extant | native | yes | |||
Andorra | extant | native | yes | |||
Armenia | extant | native | yes | |||
Australia | extant | native | yes | yes | ||
Austria | extant | native | yes | |||
Azerbaijan | extant | native | yes | |||
Bahrain | extant | native | yes | yes | ||
Bangladesh | extant | native | yes | yes | ||
Belarus | extant | native | yes | |||
Belgium | extant | native | yes | |||
Bhutan | extant | native | yes | |||
Bosnia and Herzegovina | extant | native | yes | |||
British Indian Ocean Territory | extant | native | yes | |||
Brunei | extant | native | yes | |||
Bulgaria | extant | native | yes | |||
Cambodia | extant | native | yes | yes | ||
Cameroon | extant | native | yes | |||
Central African Republic | extant | native | yes | |||
Chad | extant | native | yes | |||
Chile | extant | native | yes | |||
China (mainland) | extant | native | yes | yes | ||
Christmas Island (to Australia) | extant | native | yes | |||
Cocos (Keeling) Islands (to Australia) | extant | native | yes | |||
Congo, The Democratic Republic of the | extant | native | yes | |||
Croatia | extant | native | yes | |||
Cyprus | extant | native | yes | |||
Czechia | extant | native | yes | |||
Denmark | extant | native | yes | |||
Djibouti | extant | native | yes | yes | ||
Egypt | extant | native | yes | yes | ||
Eritrea | extant | native | yes | yes | ||
Estonia | extant | native | yes | |||
Ethiopia | extant | native | yes | |||
Faroe Islands (to Denmark) | extant | vagrant | ||||
Finland | extant | native | yes | yes | ||
France | extant | native | yes | |||
Georgia | extant | native | yes | |||
Germany | extant | native | yes | |||
Greece | extant | native | yes | |||
Hong Kong (China) | extant | native | yes | yes | ||
Hungary | extant | native | yes | |||
Iceland | extant | vagrant | ||||
India | extant | native | yes | yes | ||
Indonesia | extant | native | yes | yes | ||
Iran, Islamic Republic of | extant | native | yes | yes | ||
Iraq | extant | native | yes | yes | ||
Ireland | extant | native | yes | |||
Israel | extant | native | yes | |||
Italy | extant | native | yes | |||
Japan | extant | native | yes | |||
Jordan | extant | native | yes | |||
Kazakhstan | extant | native | yes | |||
Kenya | extant | native | yes | yes | ||
Kuwait | extant | native | yes | yes | ||
Kyrgyzstan | extant | native | yes | |||
Laos | extant | native | yes | |||
Latvia | extant | native | yes | |||
Lebanon | extant | native | yes | |||
Libya | extant | native | yes | |||
Liechtenstein | extant | native | yes | |||
Lithuania | extant | native | yes | |||
Luxembourg | extant | native | yes | |||
Macao (China) | extant | native | yes | |||
Malaysia | extant | native | yes | yes | ||
Maldives | extant | native | yes | |||
Mali | extant | native | yes | |||
Malta | extant | native | yes | |||
Mauritania | extant | vagrant | ||||
Moldova | extant | native | yes | |||
Monaco | extant | native | yes | |||
Mongolia | extant | native | yes | |||
Montenegro | extant | native | yes | |||
Morocco | extant | native | yes | |||
Mozambique | extant | vagrant | ||||
Myanmar | extant | native | yes | yes | ||
Nepal | extant | native | yes | |||
Netherlands | extant | native | yes | |||
New Zealand | extant | vagrant | ||||
Niger | extant | native | yes | |||
Nigeria | extant | native | yes | |||
North Korea | extant | native | yes | |||
North Macedonia | extant | native | yes | |||
Norway | extant | native | yes | yes | ||
Oman | extant | native | yes | yes | ||
Pakistan | extant | native | yes | yes | ||
Palau | extant | native | yes | |||
Palestine | extant | native | yes | |||
Papua New Guinea | extant | native | yes | yes | ||
Philippines | extant | native | yes | yes | ||
Poland | extant | native | yes | |||
Portugal | extant | native | yes | |||
Qatar | extant | native | yes | yes | ||
Romania | extant | native | yes | |||
Russia | extant | native | yes | yes | ||
Russia (Asian) | extant | native | yes | yes | ||
Russia (Central Asian) | extant | native | yes | yes | ||
Russia (European) | extant | native | yes | yes | ||
Rwanda | extant | vagrant | ||||
San Marino | extant | native | yes | |||
Saudi Arabia | extant | native | yes | yes | ||
Serbia | extant | native | yes | |||
Seychelles | extant | native | yes | |||
Singapore | extant | native | yes | yes | ||
Slovakia | extant | native | yes | |||
Slovenia | extant | native | yes | |||
Solomon Islands | extant | vagrant | ||||
Somalia | extant | native | yes | |||
South Africa | extant | vagrant | ||||
South Korea | extant | native | yes | |||
South Sudan | extant | native | yes | |||
Spain | extant | native | yes | |||
Sri Lanka | extant | native | yes | yes | ||
Sudan | extant | native | yes | yes | ||
Svalbard and Jan Mayen Islands (to Norway) | extant | vagrant | ||||
Sweden | extant | native | yes | yes | ||
Switzerland | extant | native | yes | |||
Syria | extant | vagrant | yes | |||
Taiwan, China | extant | native | yes | yes | ||
Tajikistan | extant | native | yes | |||
Tanzania | extant | native | yes | |||
Thailand | extant | native | yes | yes | ||
Timor-Leste | extant | native | yes | yes | ||
Tunisia | extant | native | yes | |||
Türkiye | extant | native | yes | |||
Turkmenistan | extant | native | yes | |||
Uganda | extant | native | yes | |||
Ukraine | extant | native | yes | |||
United Arab Emirates | extant | native | yes | yes | ||
United Kingdom | extant | native | yes | |||
USA | extant | vagrant | ||||
Uzbekistan | extant | native | yes | |||
Vatican City | extant | native | yes | |||
Vietnam | extant | native | yes | yes | ||
Yemen | extant | native | yes | yes | ||
Zambia | extant | vagrant |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Aquatic & Marine | Artificial/Aquatic - Irrigated Land (includes irrigation channels) | suitable | passage |
Artificial/Aquatic & Marine | Artificial/Aquatic - Salt Exploitation Sites | major | non-breeding |
Artificial/Aquatic & Marine | Artificial/Aquatic - Seasonally Flooded Agricultural Land | suitable | passage |
Artificial/Aquatic & Marine | Artificial/Aquatic - Wastewater Treatment Areas | suitable | non-breeding |
Marine Coastal/Supratidal | Coastal Brackish/Saline Lagoons/Marine Lakes | major | non-breeding |
Marine Coastal/Supratidal | Coastal Freshwater Lakes | suitable | non-breeding |
Marine Intertidal | Mud Flats and Salt Flats | major | non-breeding |
Marine Intertidal | Salt Marshes (Emergent Grasses) | suitable | non-breeding |
Wetlands (inland) | Bogs, Marshes, Swamps, Fens, Peatlands | suitable | passage |
Wetlands (inland) | Bogs, Marshes, Swamps, Fens, Peatlands | major | breeding |
Wetlands (inland) | Permanent Freshwater Lakes (over 8ha) | suitable | non-breeding |
Wetlands (inland) | Permanent Freshwater Marshes/Pools (under 8ha) | suitable | non-breeding |
Wetlands (inland) | Seasonal/Intermittent Freshwater Marshes/Pools (under 8ha) | suitable | non-breeding |
Wetlands (inland) | Tundra Wetlands (incl. pools and temporary waters from snowmelt) | major | breeding |
Altitude | 0 - 2000 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Marine & freshwater aquaculture - Scale Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Fishing & harvesting aquatic resources - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Biological resource use | Fishing & harvesting aquatic resources - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Unintentional effects (species is not the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Energy production & mining | Oil & gas drilling | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Energy production & mining | Renewable energy | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Human intrusions & disturbance | Recreational activities | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Spartina alterniflora | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Pollution | Agricultural & forestry effluents - Type Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Residential & commercial development | Commercial & industrial areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Broad-billed Sandpiper Calidris falcinellus. Downloaded from
https://datazone.birdlife.org/species/factsheet/broad-billed-sandpiper-calidris-falcinellus on 24/11/2024.
Recommended citation for factsheets for more than one species: BirdLife International (2024) IUCN Red List for birds. Downloaded from
https://datazone.birdlife.org/species/search on 24/11/2024.