|Scientific Name:||Coccothraustes coccothraustes (Linnaeus, 1758)|
|Taxonomic Source(s):||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.|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Reviewer(s):||Butchart, S. & Symes, A.|
|Facilitator/Compiler(s):||Ashpole, J, Butchart, S., Ekstrom, J.|
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). The population trend appears to be increasing, and hence the species does not approach the thresholds for Vulnerable under the population trend criterion (>30% decline over ten years or three generations). The population size is extremely 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:|
Native:Afghanistan; Albania; Algeria; Andorra; Armenia; Austria; Azerbaijan; Belarus; Belgium; Bosnia and Herzegovina; Bulgaria; China; Croatia; Cyprus; Czech Republic; Denmark; Egypt; Estonia; Finland; France; Georgia; Germany; Greece; Hungary; Iran, Islamic Republic of; Iraq; Israel; Italy; Japan; Jordan; Kazakhstan; Korea, Democratic People's Republic of; Korea, Republic of; Kyrgyzstan; Latvia; Lebanon; Libya; Liechtenstein; Lithuania; Luxembourg; Macedonia, the former Yugoslav Republic of; Malta; Moldova; Mongolia; Montenegro; Morocco; Netherlands; Norway; Poland; Portugal; Romania; Russian Federation (Central Asian Russia, Eastern Asian Russia, European Russia); Serbia; Slovakia; Slovenia; Spain (Canary Is.); Svalbard and Jan Mayen; Sweden; Switzerland; Taiwan, Province of China; Tajikistan; Tunisia; Turkey; Turkmenistan; Ukraine; United Kingdom; Uzbekistan
Vagrant:Faroe Islands; Gibraltar; Ireland; Saudi Arabia; Syrian Arab Republic; United States
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||In Europe, the breeding population is estimated to number 2,600,000-5,070,000 pairs, which equates to 5,200,000-10,100,000 mature individuals (BirdLife International 2015). Europe forms c.50% of the global range, so a very preliminary estimate of the global population size is 10,400,000-20,200,000 mature individuals, although further validation of this estimate is needed.|
Trend Justification: In Europe, trends between 1980 and 2013 showed a moderate increase (EBCC 2015).
|Current Population Trend:||Increasing|
|Habitat and Ecology:||This species prefers broadleaved forest, in particular oak-hornbeam, and also mixed forest. Besides more natural forests it also occupies parks and gardens, Prunus (cherry) orchards and olive groves in some areas of its range. In the drier southern parts of its range it inhabits steppe-woodlands and thorn thickets. It breeds up to 1,300 m in central Europe and up to 2,200 m asl in the Caucasus (Hagemeijer and Blair 1997, Calladine and Morrison 2010, Clement and Christie 2016). |
The breeding season is between the end of March and mid-August. The species is monogamous, forming pair-bonds for more than one year. It occasionally breeds in small colonies. The nest is built by both parents, in a tree up to 14 m. The clutch size is normally three to five eggs but may be even larger in some areas with optimal habitat conditions. The eggs are incubated by the female for 11–13 days. The chicks are reared by both parents and leave the nest after 11–13 days and become independent after about 30 days (Hagemeijer and Blair 1997, Tomiałojć 2012, Clement and Christie 2016). The diet of the species consists predominantly of seeds, buds and shoots of trees and shrubs. In particular the nestlings are fed by small invertebrates. Food is collected at all levels in trees and also on the ground (Clement and Christie 2016). The species is resident and migratory. Asian populations are largely migratory whereas in northern and central Europe the species is sedentary, locally dispersive or partially migratory (Clement and Christie 2016).
|Continuing decline in area, extent and/or quality of habitat:||Unknown|
|Generation Length (years):||5.5|
|Movement patterns:||Full Migrant|
|Major Threat(s):||Generally there is no evidence for substantial threats at least within its European range. Since the 1990s the species has expanded its European range. Declines in some countries are possibly related to destruction of deciduous forest, removal of old orchards and increased predation (BirdLife International 2015, Clement and Christie 2016).|
Conservation Actions Underway
The species was added to the British list of Birds of Conservation Concern in 2009 (Eaton et al. 2009).
Conservation Actions Proposed
Further research is needed to determine the factors which are affecting this species and then identify potential management methods to counter these (Eaton et al. 2009).
|Amended reason:||Map revised.|
|Citation:||BirdLife International. 2017. Coccothraustes coccothraustes (amended version of 2016 assessment). The IUCN Red List of Threatened Species 2017: e.T22720681A111132393.Downloaded on 22 April 2018.|
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