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The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T22693336A38834283 Arenaria interpres, Ruddy Turnstone Assessment by: BirdLife International View on www.iucnredlist.org Citation: BirdLife International. 2012. Arenaria interpres. The IUCN Red List of Threatened Species 2012: e.T22693336A38834283. http://dx.doi.org/10.2305/IUCN.UK.20121.RLTS.T22693336A38834283.en Copyright: © 2015 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale, reposting or other commercial purposes is prohibited without prior written permission from the copyright holder. For further details see Terms of Use. The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. The IUCN Red List Partners are: BirdLife International; Botanic Gardens Conservation International; Conservation International; Microsoft; NatureServe; Royal Botanic Gardens, Kew; Sapienza University of Rome; Texas A&M University; Wildscreen; and Zoological Society of London. If you see any errors or have any questions or suggestions on what is shown in this document, please provide us with feedback so that we can correct or extend the information provided. THE IUCN RED LIST OF THREATENED SPECIES™ Taxonomy Kingdom Phylum Class Order Family Animalia Chordata Aves Charadriiformes Scolopacidae Taxon Name: Arenaria interpres (Linnaeus, 1758) Regional Assessments: • Europe Common Name(s): • English: • French: Ruddy Turnstone, Turnstone Tournepierre à collier 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. Assessment Information Red List Category & Criteria: Least Concern ver 3.1 Year Published: 2012 Date Assessed: May 1, 2012 Justification: This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence <20,000 km2 combined with a declining or fluctuating range size, habitat extent/quality, or population size and a small number of locations or severe fragmentation). Despite the fact that the population trend appears to be decreasing, the decline is not believed to be sufficiently rapid to approach the thresholds for Vulnerable under the population trend criterion (>30% decline over ten years or three generations). The population size is very large, and hence does not approach the thresholds for Vulnerable under the population size criterion (<10,000 mature individuals with a continuing decline estimated to be >10% in ten years or three generations, or with a specified population structure). For these reasons the species is evaluated as Least Concern. Previously Published Red List Assessments 2009 – Least Concern (LC) 2008 – Least Concern (LC) 2004 – Least Concern (LC) 2000 – Lower Risk/least concern (LR/lc) 1994 – Lower Risk/least concern (LR/lc) 1988 – Lower Risk/least concern (LR/lc) © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 1 Geographic Range Country Occurrence: Native: Afghanistan; Albania; Algeria; American Samoa (American Samoa); Angola (Angola); Anguilla; Antigua and Barbuda; Argentina; Armenia (Armenia); Aruba; Australia; Austria; Azerbaijan; Bahamas; Bahrain; Bangladesh; Barbados; Belgium; Belize; Benin; Bermuda; Bolivia, Plurinational States of; Bonaire, Sint Eustatius and Saba; Botswana; Brazil; British Indian Ocean Territory; Brunei Darussalam; Bulgaria; Burkina Faso; Burundi; Cambodia; Cameroon; Canada; Cape Verde; Cayman Islands; Chad; Chile; China; Christmas Island; Cocos (Keeling) Islands; Colombia; Comoros; Congo; Congo, The Democratic Republic of the; Cook Islands; Costa Rica; Côte d'Ivoire; Croatia; Cuba; Curaçao; Cyprus; Czech Republic; Denmark; Djibouti; Dominica; Dominican Republic; Ecuador; Egypt; El Salvador; Equatorial Guinea; Eritrea; Estonia; Ethiopia; Falkland Islands (Malvinas); Faroe Islands; Fiji; Finland; France; French Guiana; French Polynesia; French Southern Territories; Gabon; Gambia; Georgia; Germany; Ghana; Gibraltar; Greece; Greenland; Grenada; Guadeloupe; Guam; Guatemala; Guinea; Guinea-Bissau; Guyana; Haiti; Honduras; Hong Kong; Hungary; Iceland; India; Indonesia; Iran, Islamic Republic of; Iraq; Ireland; Israel; Italy; Jamaica; Japan; Jordan; Kazakhstan; Kenya; Kiribati; Korea, Democratic People's Republic of; Korea, Republic of; Kuwait; Kyrgyzstan; Latvia; Lebanon; Liberia; Libya; Lithuania; Macedonia, the former Yugoslav Republic of; Madagascar; Malawi; Malaysia; Maldives; Mali; Malta; Marshall Islands; Martinique; Mauritania; Mauritius; Mayotte; Mexico; Micronesia, Federated States of ; Mongolia; Montenegro; Montserrat; Morocco; Mozambique; Myanmar; Namibia; Nauru; Nepal; Netherlands; New Caledonia; New Zealand; Nicaragua; Niger; Nigeria; Niue; Norfolk Island; Northern Mariana Islands; Norway; Oman; Pakistan; Palau; Palestinian Territory, Occupied; Panama; Papua New Guinea; Peru; Philippines; Poland; Portugal; Puerto Rico; Qatar; Réunion; Romania; Russian Federation; Saint Helena, Ascension and Tristan da Cunha; Saint Kitts and Nevis; Saint Lucia; Saint Martin (French part); Saint Pierre and Miquelon; Saint Vincent and the Grenadines; Samoa; Sao Tomé and Principe; Saudi Arabia; Senegal; Serbia (Serbia); Seychelles; Sierra Leone; Singapore; Sint Maarten (Dutch part); Slovakia; Solomon Islands; Somalia; South Africa; South Georgia and the South Sandwich Islands; South Sudan; Spain; Sri Lanka; Sudan; Suriname; Svalbard and Jan Mayen; Sweden; Switzerland; Taiwan, Province of China; Tajikistan; Tanzania, United Republic of; Thailand; Timor-Leste; Togo; Tokelau; Tonga; Trinidad and Tobago; Tunisia; Turkey; Turkmenistan; Turks and Caicos Islands; Tuvalu; Uganda; Ukraine; United Arab Emirates; United Kingdom; United States (Georgia); United States Minor Outlying Islands; Uruguay; Uzbekistan; Vanuatu; Venezuela, Bolivarian Republic of; Viet Nam; Virgin Islands, British; Virgin Islands, U.S.; Western Sahara; Yemen; Zambia; Zimbabwe Vagrant: Belarus; Lesotho; Liechtenstein; Luxembourg; Paraguay; Rwanda; Slovenia; Swaziland © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 2 Distribution Map © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 3 Population The global population is estimated to number c.460,000-800,000 individuals (Wetlands International, 2006), while national population estimates include: c.1,000-10,000 individuals on migration and c.501,000 wintering individuals in China; c.1,000-10,000 individuals on migration and c.50-10,000 wintering individuals in Taiwan; c.50-10,000 individuals on migration in Korea; c.1,000-10,000 individuals on migration and c.50-1,000 wintering individuals in Japan and c.10,000-100,000 breeding pairs and c.1,000-10,000 individuals on migration in Russia (Brazil 2009). Trend Justification The overall population trend is decreasing, although some populations have unknown trends (Wetlands International 2006), and in North America the trend is increasing (based on BBS/CBC data: Butcher and Niven 2007). Current Population Trend: Decreasing Habitat and Ecology (see Appendix for additional information) Behaviour This species is fully migratory (del Hoyo et al. 1996). It breeds from May to early-August (Hayman et al. 1986) in solitary pairs (del Hoyo et al. 1996), although several pairs may nest close together in optimal habitats (Johnsgard 1981) along coasts or on islands (Snow and Perrins 1998). The species migrates in large flocks (del Hoyo et al. 1996) and is gregarious and sociable when feeding or roosting in winter (Snow and Perrins 1998), often foraging in close flocks of 10-100 or more individuals, especially in tidal areas (del Hoyo et al. 1996). Habitat Breeding The species breeds near the coast or up to several kilometres inland (Snow and Perrins 1998) in the high Arctic (Hayman et al. 1986), nesting on coastal plains, marshes and tundra (del Hoyo et al. 1996) and showing a preference for mosaics of bare rock, clay or shingle and vegetation near water (Snow and Perrins 1998) or in areas that remain damp until late summer (Johnsgard 1981). Non-breeding Outside of the breeding season the species is mainly coastal (del Hoyo et al. 1996), although on migration it may occur inland along dykes or on lake shores (del Hoyo et al. 1996). During the winter it frequents productive rocky and shingle shores (Hayman et al. 1986, del Hoyo et al. 1996), breakwaters (del Hoyo et al. 1996), sandy beaches with storm-wracked seaweed (Hayman et al. 1986, del Hoyo et al. 1996), short-grass saltmarshes, sheltered inlets, estuaries, mangroves swamps, exposed reefs and mudflats with beds of molluscs (del Hoyo et al. 1996). Diet Breeding On its Arctic breeding grounds the species takes Diptera(especially adult and larval midges) as well as larval Lepidoptera, Hymenoptera, Coleoptera and spiders, occasionally also taking vegetable matter early in the season (del Hoyo et al. 1996). Non-breeding Outside of the breeding season its diet consists of insects, crustaceans, molluscs (del Hoyo et al. 1996) (especially mussels or cockles) (Johnsgard 1981), annelids, echinoderms, small fish, carrion and birds eggs (del Hoyo et al. 1996). Breeding site The nest is a shallow depression (del Hoyo et al. 1996) in mud, peat or on dry ground (Johnsgard 1981) with dense vegetation (del Hoyo et al. 1996), often positioned on a slight ridge, hummock or tussock, or in cleft or shallow fissure (Snow and Perrins 1998). The species usually nests solitarily, although neighbouring pairs may nest as little as 15 m apart along coasts or on islands (where abundant feeding habitats are available) (Snow and Perrins 1998). Management information Removing feral American mink Neovison vison from a large archipelago with many small islands in the Baltic Sea had the result of increasing the breeding density of this species in the area (Nordstrom et al. 2003). Systems: Terrestrial, Freshwater, Marine © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 4 Threats (see Appendix for additional information) The species suffers nest predation from feral American mink Neovison vison in some regions (Nordstrom et al. 2003), and is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Credits Assessor(s): BirdLife International Reviewer(s): Butchart, S. & Symes, A. Facilitators(s) and Compiler(s): Ekstrom, J., Butchart, S., Malpas, L. © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 5 Bibliography Brazil, M. 2009. Birds of East Asia: eastern China, Taiwan, Korea, Japan, eastern Russia. Christopher Helm, London. Delany, S.; Scott, D. 2006. Waterbird population estimates. Wetlands International, Wageningen, The Netherlands. del Hoyo, J., Elliott, A., and Sargatal, J. 1996. Handbook of the Birds of the World, vol. 3: Hoatzin to Auks. Lynx Edicions, Barcelona, Spain. Hayman, P.; Marchant, J.; Prater, A. J. 1986. Shorebirds. Croom Helm, London. IUCN. 2012. IUCN Red List of Threatened Species (ver. 2012.1). Available at: http://www.iucnredlist.org. (Accessed: 19 June 2012). Johnsgard, P. A. 1981. The plovers, sandpipers and snipes of the world. University of Nebraska Press, Lincoln, U.S.A. and London. Melville, D. S.; Shortridge, K. F. 2006. Migratory waterbirds and avian influenza in the East AsianAustralasian Flyway with particular reference to the 2003-2004 H5N1 outbreak. In: Boere, G.; Galbraith, C., Stroud, D. (ed.), Waterbirds around the world, pp. 432-438. The Stationary Office, Edinburgh, UK. Nordström, M.; Högmander, J.; Nummelin, J.; Laine, J.; Laanetu, N.; Korpimäki, E. 2003. Effects of feral mink removal on seabirds, waders and passerines on small islands in the Baltic Sea. Biological Conservation 109: 359-368. Snow, D.W. and Perrins, C.M. 1998. The Birds of the Western Palearctic, Volume 1: Non-Passerines. Oxford University Press, Oxford. Citation BirdLife International. 2012. Arenaria interpres. The IUCN Red List of Threatened Species 2012: e.T22693336A38834283. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en Disclaimer To make use of this information, please check the Terms of Use. External Resources For Images and External Links to Additional Information, please see the Red List website. © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 6 Appendix Habitats (http://www.iucnredlist.org/technical-documents/classification-schemes) Habitat Season Suitability Major Importance? 4. Grassland -> 4.1. Grassland - Tundra Breeding Suitable Yes 5. Wetlands (inland) -> 5.1. Wetlands (inland) - Permanent Rivers/Streams/Creeks (includes waterfalls) Nonbreeding Suitable No 5. Wetlands (inland) -> 5.4. Wetlands (inland) - Bogs, Marshes, Swamps, Fens, Peatlands Breeding Suitable No 5. Wetlands (inland) -> 5.5. Wetlands (inland) - Permanent Freshwater Lakes (over 8ha) Nonbreeding Suitable No 5. Wetlands (inland) -> 5.6. Wetlands (inland) - Seasonal/Intermittent Freshwater Lakes (over 8ha) Nonbreeding Suitable No 5. Wetlands (inland) -> 5.10. Wetlands (inland) - Tundra Wetlands (incl. pools and temporary waters from snowmelt) Breeding Suitable Yes 9. Marine Neritic -> 9.8. Marine Neritic - Coral Reef -> 9.8.1. Outer Reef Channel Nonbreeding Suitable No 9. Marine Neritic -> 9.8. Marine Neritic - Coral Reef -> 9.8.2. Back Slope Nonbreeding Suitable No 9. Marine Neritic -> 9.8. Marine Neritic - Coral Reef -> 9.8.3. Foreslope (Outer Reef Slope) Nonbreeding Suitable No 9. Marine Neritic -> 9.8. Marine Neritic - Coral Reef -> 9.8.4. Lagoon Nonbreeding Suitable No 9. Marine Neritic -> 9.8. Marine Neritic - Coral Reef -> 9.8.5. Inter-Reef Soft Substrate Nonbreeding Suitable No 9. Marine Neritic -> 9.8. Marine Neritic - Coral Reef -> 9.8.6. Inter-Reef Rubble Substrate Nonbreeding Suitable No 9. Marine Neritic -> 9.10. Marine Neritic - Estuaries Nonbreeding Suitable No 12. Marine Intertidal -> 12.1. Marine Intertidal - Rocky Shoreline Nonbreeding Suitable No 12. Marine Intertidal -> 12.2. Marine Intertidal - Sandy Shoreline and/or Beaches, Sand Bars, Spits, Etc Nonbreeding Suitable No 12. Marine Intertidal -> 12.3. Marine Intertidal - Shingle and/or Pebble Shoreline and/or Beaches Nonbreeding Suitable No 12. Marine Intertidal -> 12.4. Marine Intertidal - Mud Flats and Salt Flats Nonbreeding Suitable No 12. Marine Intertidal -> 12.5. Marine Intertidal - Salt Marshes (Emergent Grasses) Nonbreeding Suitable No © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 7 Habitat Season Suitability Major Importance? 12. Marine Intertidal -> 12.6. Marine Intertidal - Tidepools Nonbreeding Suitable No Use and Trade (http://www.iucnredlist.org/technical-documents/classification-schemes) End Use Local National International Food - human Yes Yes No Pets/display animals, horticulture No No Yes Sport hunting/specimen collecting Yes Yes No Threats (http://www.iucnredlist.org/technical-documents/classification-schemes) Threat Timing Scope Severity Impact Score 11. Climate change & severe weather -> 11.1. Habitat shifting & alteration Future Whole (>90%) Unknown - Stresses: 1. Ecosystem stresses -> 1.2. Ecosystem degradation 1. Ecosystem stresses -> 1.3. Indirect ecosystem effects Conservation Actions in Place (http://www.iucnredlist.org/technical-documents/classification-schemes) Conservation Actions in Place In-Place Research, Monitoring and Planning Action Recovery plan: No Systematic monitoring scheme: Yes In-Place Land/Water Protection and Management Conservation sites identified: Yes, over entire range Occur in at least one PA: Yes Invasive species control or prevention: No In-Place Species Management Successfully reintroduced or introduced beningly: No Subject to ex-situ conservation: No In-Place Education Subject to recent education and awareness programmes: No © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 8 Conservation Actions in Place Included in international legislation: Yes Subject to any international management/trade controls: No Additional Data Fields Distribution Continuing decline in area of occupancy (AOO): Unknown Extreme fluctuations in area of occupancy (AOO): No Estimated extent of occurrence (EOO) (km²): 2620000 Continuing decline in extent of occurrence (EOO): Unknown Extreme fluctuations in extent of occurrence (EOO): No Continuing decline in number of locations: Unknown Extreme fluctuations in the number of locations: No Population Continuing decline of mature individuals: Unknown Extreme fluctuations: No Population severely fragmented: No Continuing decline in subpopulations: Unknown Extreme fluctuations in subpopulations: No All individuals in one subpopulation: No Habitats and Ecology Continuing decline in area, extent and/or quality of habitat: Unknown Generation Length (years): 7.3 Movement patterns: Full Migrant Congregatory: Congregatory (and dispersive) © The IUCN Red List of Threatened Species: Arenaria interpres – published in 2012. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22693336A38834283.en 9 The IUCN Red List Partnership The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. The IUCN Red List Partners are: BirdLife International; Botanic Gardens Conservation International; Conservation International; Microsoft; NatureServe; Royal Botanic Gardens, Kew; Sapienza University of Rome; Texas A&M University; Wildscreen; and Zoological Society of London. THE IUCN RED LIST OF THREATENED SPECIES™