![]() ![]() The cookie is used to store the user consent for the cookies in the category "Performance". ![]() This cookie is set by GDPR Cookie Consent plugin. The cookie is used to store the user consent for the cookies in the category "Other. The cookies is used to store the user consent for the cookies in the category "Necessary". The cookie is set by GDPR cookie consent to record the user consent for the cookies in the category "Functional". The cookie is used to store the user consent for the cookies in the category "Analytics". These cookies ensure basic functionalities and security features of the website, anonymously. Haute Soule : massif de la Pierre-St-Martin.Necessary cookies are absolutely essential for the website to function properly. Haute Soule : Forêt d'Irraty, Organbidexka et Pic des Escaliers Haute Soule : Massif Forestier, Gorges d'Holzarte et d'Olhadubi Northern slope of Guadarrama mountain rangeĬonfluent des vallées de la Meuse et de la Chiers ![]() Lower course of the river Matarraña-Ribarroja Plain between Cáceres and Trujillo-Aldea del Cano North and east coasts of Minorca and island of Aire National Park of Dadia - Lefkimi - Soufli forest Mesolongi and Aitoliko lagoons, Acheloos delta and Evinos estuary Serra de Penha Garcia e Campina de ToulõesĪrchipelago and coastline of North-East ScaniaĪxios, Loudias and Aliakmonas rivers' deltas Important Bird and Biodiversity Areas (IBA) Country/TerritoryĬonfluence of the Morava (March) and Dyje (Thaya) rivers - Tvrdonicko 2020).Ĭountry/territory distribution Country/Territory Small numbers continue to occur in winter (Radi et al. In addition, in Morocco it is believed to be extinct as a breeding species: 20 pairs were known in 1987 (Bergier 1987) but numbers declined with the last known nest located in 2004 (Radi et al. 2020). Only in Portugal was the species determined to be decreasing (BirdLife International in prep.). 2017) and Spain (Molina 2015: though declines continue in the south). Data collated from across the range and submitted to the European Commission (EC) under Article 12 of the EU Birds Directive in late 2019 indicates that the species is now stable or increasing in the majority of countries in which it occurs, including Germany (Grüneberg & Karthäuser 2019), France (David et al. A decline occurred within core breeding areas - Spain, France and Germany - between 1990 and at the early 2000s, but these were partly offset by rapid increases in the U.K., Sweden, Poland and Switzerland. Trend justification: Although this species declined globally until the 1970s owing to persecution, many populations recovered or stabilised during 1970-1990 (Mionnet 2007) and its overall numbers were probably stable in Europe from 1970 to 1990 (Tucker and Heath 1994). This is a substantial increase from the numbers previously reported: 25,200-33,400 pairs for the European Red List of Birds (BirdLife International 2015), and 21,000-25,000 pairs in 2009. The global population is therefore estimated to be between 60,000-70,000 mature individuals. Population justification: Recent data submitted to the European Commission for EU countries (which hold at least 90% of the global population) estimated a total of 29,746- 34,751 pairs breeding in 17 countries (BirdLife International in prep.), closely matching a new global estimate of c. Decline (10 years/3 generation past and future)
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