Circus Aeruginosus

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Circus Aeruginosus Circus aeruginosus -- (Linnaeus, 1758) ANIMALIA -- CHORDATA -- AVES -- ACCIPITRIFORMES -- ACCIPITRIDAE Common names: Western Marsh-harrier; Busard des roseaux; Eurasian Marsh Harrier; Marsh Harrier; Western Marsh Harrier European Red List Assessment European Red List Status LC -- Least Concern, (IUCN version 3.1) Assessment Information Year published: 2015 Date assessed: 2015-03-31 Assessor(s): BirdLife International Reviewer(s): Symes, A. Compiler(s): Ashpole, J., Burfield, I., Ieronymidou, C., Pople, R., Wheatley, H. & Wright, L. Assessment Rationale European regional assessment: Least Concern (LC) EU27 regional assessment: Least Concern (LC) At both European and EU27 scales this species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence 10% in ten years or three generations, or with a specified population structure). 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). For these reasons the species is evaluated as Least Concern within both Europe and the EU27. Occurrence Countries/Territories of Occurrence Native: Albania; Armenia; Austria; Azerbaijan; Belarus; Belgium; Bosnia and Herzegovina; Bulgaria; Croatia; Cyprus; Czech Republic; Denmark; Estonia; Finland; France; Georgia; Germany; Greece; Hungary; Ireland, Rep. of; Italy; Latvia; Liechtenstein; Lithuania; Luxembourg; Macedonia, the former Yugoslav Republic of; Malta; Moldova; Montenegro; Netherlands; Norway; Poland; Portugal; Romania; Russian Federation; Serbia; Slovakia; Slovenia; Spain; Canary Is. (to ES); Sweden; Switzerland; Turkey; Ukraine; United Kingdom; Gibraltar (to UK) Vagrant: Andorra; Faroe Islands (to DK); Iceland Population The European population is estimated at 99,300-184,000 breeding females, which equates to 199,000-367,000 mature individuals. The population in the EU27 is estimated at 37,700-87,800 breeding females, which equates to 75,500-176,000 mature individuals. For details of national estimates, see Supplementary PDF. Trend In Europe and the EU27 the population size is estimated to be increasing. For details of national estimates, see Supplementary PDF. Habitats and Ecology It is mainly migratory, although populations in western Europe are generally resident (Ferguson-Lees and Christie 2001, Orta et al. 2014). Migrant birds leave their breeding grounds in September and October, wintering from France south as far as sub-Saharan Africa (Orta et al. 2014). They begin their return journey in February and March, arriving in March and April (Snow and Perrins 1998, Ferguson-Lees and Christie 2001, Orta et al. 2014). Migration is generally on a broad front, although there is some concentration at a few sites (Brown et al. 1982). Hundreds of birds occasionally gather at roosting sites, sometimes with other harriers such as C. pygargus, but otherwise they are usually solitary, associating only temporarily at especially rich feeding sites (Snow and Perrins 1998, Ferguson-Lees and Christie 2001, Orta et al. 2014). They have a slightly greater tendency to be gregarious while on migration but the above still generally applies. Birds fly c.10–30 m above the ground (Brown et al. 1982). The species inhabits extensive areas of dense marsh vegetation, in fresh or brackish water, generally in lowlands (Orta et al. 2014), up to 400 m (Hagemeijer and Blair 1997). It is a generalist predator taking a variety of prey types, with small birds generally preferred but mammals such as voles, rabbits and rats being more important in parts of its range. The nest is a pile of reeds built in dense marsh vegetation. Typically lays three to six eggs (Orta et al. 2014). Habitats & Altitude Habitat (level 1 - level 2) Importance Occurrence Artificial/Terrestrial - Arable Land suitable breeding Marine Intertidal - Salt Marshes (Emergent Grasses) suitable non-breeding Wetlands (inland) - Bogs, Marshes, Swamps, Fens, Peatlands major breeding Wetlands (inland) - Bogs, Marshes, Swamps, Fens, Peatlands major non-breeding Wetlands (inland) - Permanent Freshwater Lakes (over ha) suitable breeding Wetlands (inland) - Permanent Freshwater Lakes (over ha) suitable non-breeding Wetlands (inland) - Permanent Freshwater Marshes/Pools (under ha) major breeding Wetlands (inland) - Permanent Freshwater Marshes/Pools (under ha) major non-breeding Wetlands (inland) - Permanent Inland Deltas suitable breeding Wetlands (inland) - Permanent Inland Deltas suitable non-breeding Wetlands (inland) - Seasonal/Intermittent/Irregular Rivers/Streams/Creeks suitable breeding Wetlands (inland) - Seasonal/Intermittent/Irregular Rivers/Streams/Creeks suitable non-breeding Altitude 0-400 m Occasional altitudinal limits Threats Major threats include wetland desiccation and drainage; persecution by shooting; pollution, especially from excessive pesticide use in and around wetlands, and poisoning by heavy metals, notably the consumption of lead-shot through feeding on contaminated waterbirds (Ferguson-Lees and Christie 2001, Orta et al. 2014). The historical threat of hunting in southern Europe has mostly subsided, but illegal shooting is still rife locally, notably on Malta (Ferguson-Lees and Christie 2001). The species is also highly vulnerable to the effects of potential wind energy development (Strix 2012). Threats & Impacts Threat (level 1) Threat (level 2) Impact and Stresses Biological resource Hunting & trapping Timing Scope Severity Impact use terrestrial animals Ongoing Minority (<50%) Slow, Significant Low Impact (persecution/ Declines control) Stresses Species mortality Energy production Renewable energy Timing Scope Severity Impact & mining Ongoing Minority (<50%) Slow, Significant Low Impact Declines Stresses Species mortality Natural system Abstraction of Timing Scope Severity Impact modifications surface water Ongoing Majority (50-90%) Negligible declines Low Impact (unknown use) Stresses Ecosystem conversion Pollution Herbicides and Timing Scope Severity Impact pesticides Ongoing Minority (<50%) Slow, Significant Low Impact Declines Stresses Indirect ecosystem effects Pollution Industrial & military Timing Scope Severity Impact effluents (type Ongoing Minority (<50%) Slow, Significant Low Impact unknown/ Declines unrecorded) Stresses Indirect ecosystem effects Conservation Conservation Actions Underway Bern Convention Appendix II. EU Birds Directive Annex I. CITES Appendix II. CMS Appendix II. The widespread ban of persistent pesticides has allowed the recovery of populations in some areas (Hagemeijer and Blair 1997, Orta et al. 2014). In the Netherlands, parts of the Ijsselmeer have been reclaimed, providing huge reedbeds and thus breeding and feeding habitat for the species (Hagemeijer and Blair 1997). The use of lead shot has been completely banned in Belgium, Denmark, the Netherlands and Norway and partial bans are in place in many other countries (AEWA 2009). Conservation Actions Proposed Conservation of this species’s wetland habitat is most important; existing wetlands should be legally protected and degraded wetlands restored. In agricultural areas, an unharvested area should be left around active nests of 30 m x 30 m until the chicks have fledged (Mebs and Schmidt 2006). Lead free ammunition should be banned completely across the species’s range. Bibliography AEWA (2009). Phasing out the use of lead shot for hunting in wetland: Experiences made and lessons learned by AEWA range states. Secretariat of the Agreement on the Conservation of African-Eurasian Migratory Waterbirds (UNEP/AEWA). Brown, L. H.; Urban, E. K.; Newman, K. 1982. The birds of Africa vol I. Academic Press, London. Ferguson-Lees, J.; Christie, D. A. 2001. Raptors of the world. Christopher Helm, London. Hagemeijer, W.J.M. & Blair, M.J. (1997) The EBCC Atlas of European Breeding Birds: Their Distribution and Abundance. T & A D Poyser, London. Mebs, T. & Schmidt, D. (2006). Die Greifvögel Europas, Nordafrikas und Vorderasiens. Kosmos Verlag. Orta, J., Boesman, P. & Marks, J.S. (2014). Western Marsh-harrier (Circus aeruginosus). In: del Hoyo, J., Elliott, A., Sargatal, J., Christie, D.A. & de Juana, E. (eds.) (2014). Handbook of the Birds of the World Alive. Lynx Edicions, Barcelona. (retrieved from http://www.hbw.com/node/53021 on 13 March 2015). Snow, D. W.; Perrins, C. M. 1998. The Birds of the Western Palearctic vol. 1: Non-Passerines. Oxford University Press, Oxford. Strix. 2012. Developing and testing the methodology for assessing and mapping the sensitivity of migratory birds to wind energy development. BirdLife International, Cambridge. Map (see overleaf) .
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