Puffinus yelkouan -- (Acerbi, 1827) ANIMALIA -- CHORDATA -- AVES -- PROCELLARIIFORMES -- PROCELLARIIDAE Common names: Yelkouan Shearwater;

Puffinus yelkouan -- (Acerbi, 1827) ANIMALIA -- CHORDATA -- AVES -- PROCELLARIIFORMES -- PROCELLARIIDAE Common names: Yelkouan Shearwater; Assessment Information European Red List Status LC -- Least Concern, (IUCN version 3.1) European Red List Assessment 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 the range size has not been quantified, but it is not believed to approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). The population size may be moderately small to large, but it is not believed to approach the thresholds for Vulnerable under the population size criterion (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; Bosnia and Herzegovina; Bulgaria; Croatia; Cyprus; France; Georgia; Greece; Italy; Macedonia, the former Yugoslav Republic of; Malta; Romania; Russian Federation; Slovenia; Spain; Canary Is. (to ES); Turkey; Ukraine; Gibraltar (to UK) Origin Uncertain: Montenegro; United Kingdom Vagrant: Austria Population The European population is estimated at 19,400-31,200 pairs, which equates to 38,800-62,400 mature individuals. The population in the EU27 is estimated at 19,100-29,800 pairs, which equates to 38,200-59,600 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 This species is marine, frequenting mostly inshore waters. It breeds on rocky coastal and offshore islets, and on the mainland (Snow and Perrins 1998). It is a colonial breeder, nesting in rock crevices or ledges in caves, occasionally in old rabbit burrows, lined with sparse plant material. It sometimes nests on cliffs. Clutch is a single white egg. The species forages mostly by pursuit-plunging and pursuit-diving. Diet composition varies through the year but consists mostly of fish, squid and crustacea (Carboneras et al. 2014). In the non-breeding season it disperses widely within the Mediterranean and Black Seas, often congregating in large flocks (Snow

and Perrins 1998). Habitats & Altitude Habitat (level 1 - level 2) Importance Occurrence Marine Coastal/Supratidal - Sea Cliffs and Rocky Offshore Islands major breeding Marine Neritic - Macroalgal/Kelp major breeding Marine Neritic - Macroalgal/Kelp major non-breeding Marine Neritic - Pelagic major breeding Marine Neritic - Pelagic major non-breeding Marine Neritic - Seagrass (Submerged) major breeding Marine Neritic - Seagrass (Submerged) major non-breeding Marine Neritic - Subtidal Loose Rock/pebble/gravel major breeding Marine Neritic - Subtidal Loose Rock/pebble/gravel major non-breeding Marine Neritic - Subtidal Rock and Rocky Reefs major breeding Marine Neritic - Subtidal Rock and Rocky Reefs major non-breeding Marine Neritic - Subtidal Sandy major breeding Marine Neritic - Subtidal Sandy major non-breeding Marine Neritic - Subtidal Sandy-Mud major breeding Marine Neritic - Subtidal Sandy-Mud major non-breeding Marine Oceanic - Epipelagic (m) major breeding Marine Oceanic - Epipelagic (m) major non-breeding Rocky areas (eg. inland cliffs, mountain peaks) suitable breeding Altitude Occasional altitudinal limits Threats The most serious threat to the species is mortality from incidental fishing bycatch, followed by predation by invasive predators (predominantly rats (Rattus rattus) and to a lesser extent, feral cats (Felis catus)). A study in France and Malta (Oppel et al. 2011) implicated fishing bycatch as a critical cause of mortality for the species, since the majority of the adult mortality of birds breeding in Malta occurred during the non-breeding season. This pattern is consistent with the presumed cause of low adult survival probabilities in the Balearic Shearwater (Oro et al. 2004, Tavecchia et al. 2008). Long-liners in particular affect the species (Arcos et al. 2008, Louzao et al. 2011), often on an irregular basis, but impacting fairly large numbers at a time. Since Procellariiforms are generally long-lived, their populations are highly sensitive to changes in adult survival. The increased adult mortality induced by accidental bycatch is therefore a significant danger to them and a highly important threat (Lebreton 2000). These shearwaters have been shown to suffer substantial predation pressure by introduced mammalian predators on breeding grounds (Bourgeois et al. 2008, Bonnaud et al. 2009) with observed population declines in Italy being attributed to alien predators, predominantly rats (Sultana and Borg 2006, Capizzi et al. 2010), which heavily limit reproductive success by predation upon chicks and eggs. On the Tavolara archipelago, Italy, the colony size has been much reduced in the last 30 years and vast sectors of the islands have been deserted; breeding success was assessed for the first time in 2006 and it was found to be zero (due to rat predation) in several colonies (J. J. Borg in litt. 2006). Feral cats are a major threat. On the Hyères islands (French Mediterranean coast), feral cats have been identified as the primary predator of the species: shearwater remains were found in up to 6% of cat scats, representing hundreds of adults killed each year, especially during the pre-breeding period (Bourgeois and Vidal 2008). Increasing tourism and coastal urbanization in the Mediterranean create sound and light disturbances at colonies and damages fragile breeding habitats (Bourgeois and Vidal 2008, Oppel et al. 2011). Breeding success may be affected by reduced abundance of anchovies and sprats due to competition from fisheries (Bourgeois and Vidal 2008). The gregarious behaviour of this species makes it particularly vulnerable to oil spills and the intense maritime traffic in the Mediterranean and Bosporus increases the risk of oil spills. Less prominent threats include competition for nest sites with Cory's Shearwater, collisions with wind turbines, pollution and contaminants (e.g. plastic (R. Crnkovic in litt. 2012)), environmental events (such as toxic algal blooms and geological erosion) and illegal hunting (Derhé 2012).

Threats & Impacts Threat (level 1) Threat (level 2) Impact and Biological resource Fishing & harvesting Timing Scope Severity Impact use aquatic resources Ongoing Majority (50-90%) Slow, Significant Medium Impact (unintentional effects: (large scale) [harvest]) Species mortality; Competition; Reduced reproductive success Biological resource Fishing & harvesting Timing Scope Severity Impact use aquatic resources Ongoing Majority (50-90%) Slow, Significant Medium Impact (unintentional effects: (subsistence/small scale) [harvest]) Species mortality; Competition; Reduced reproductive success Biological resource Hunting & trapping Timing Scope Severity Impact use terrestrial animals Past, Unlikely to Majority (50-90%) Slow, Significant Past Impact (intentional use - Return species is the target) Species mortality Energy production Renewable energy Timing Scope Severity Impact & mining Ongoing Minority (<50%) Slow, Significant Low Impact Species mortality Geological events Avalanches/ Timing Scope Severity Impact landslides Ongoing Minority (<50%) Slow, Significant Low Impact Ecosystem degradation Invasive and other Black Rat (Rattus Timing Scope Severity Impact problematic rattus) Ongoing Majority (50-90%) Slow, Significant Medium Impact species, genes & diseases Species mortality; Reduced reproductive success Invasive and other Domestic Cat (Felis Timing Scope Severity Impact problematic catus) Ongoing Minority (<50%) Slow, Significant Low Impact species, genes & diseases Species mortality; Reduced reproductive success Invasive and other Unspecified species Timing Scope Severity Impact problematic Ongoing Minority (<50%) Causing/Could Low Impact species, genes & cause fluctuations diseases Competition Pollution Industrial & military Timing Scope Severity Impact effluents (type Ongoing Unknown Causing/Could Unknown unknown/ cause fluctuations unrecorded) Reduced reproductive success Pollution Oil spills Timing Scope Severity Impact Future Minority (<50%) Rapid Low Impact Species mortality Residential & Tourism & Timing Scope Severity Impact commercial recreation areas Ongoing Majority (50-90%) Slow, Significant development Medium Impact Ecosystem conversion; Ecosystem degradation; Species disturbance Conservation Actions Underway Conservation

EU Birds Directive Annex I. Annex II of the Bern Convention. A new IBA project has been started in Malta. An EU Life/BirdLife Malta project aimed at conserving a colony of c. 500 pairs at Rdumtal-Madonna, Malta, has recently been completed. A rat eradication project is being implemented at Montecristo Island, Italy during 2011 2012 as part of the 2010 Montecristo LIFE project that aims to eradicate several invasive species from Montecristo and Pianosa (see http://www.montecristo2010.it/index.asp). Conservation Actions Proposed Determine whether the species breeds in Turkey. Search for colonies at sites in Turkey and Greece. Carry out population censuses at breeding colonies for which there is currently little reliable, up-to-date population size data, particularly those in Sicily, Sardinia and Greece. Continue breeding and non-breeding period counts at the Bosporus and conduct breeding and non-breeding counts at other bottleneck sites. Research ecological requirements and carry out extensive demographic monitoring. Research the impact of introduced predators across breeding range. Research impact of predator control/eradication programmes on annual survival and breeding success at different sites. As a precaution, control or if possible eradicate feral cats and rats at breeding colonies, according to a priority analysis and at sites with evidence of predation. Quantify extent of mortality from accidental bycatch and encourage policymakers to implement and enforce measures that reduce accidental bycatch of this species and other seabirds in commercial fishing operations in the Mediterranean and Black Seas. Identify and implement measures to reduce/mitigate the effects of light pollution on the species (e.g. Raine et al. 2007). Bibliography Arcos, J.M., Louzao, M. and Oro, D. 2008. Fishery ecosystem impacts and management in the Mediterranean: seabirds point of view. In: Nielsen, J., Dodson, J., Friedland, K., Hamon, T., Hughes, N., Musick, J. and Verspoor, E. (ed.), Proceedings of the Fourth World Fisheries Congress: Reconciling Fisheries with Conservation, pp. 587-596. American Fisheries Society, Symposium 49, Bethesda, MD, USA. Bonnaud, E., Bourgeois, K., Vidal, E., Legrand, J. and Le Corre, M. 2009. How can the Yelkouan shearwater survive feral cat predation? A meta-population structure as a solution? Population Ecology 51: 261-270. Bourgeois, K. and Vidal, E. 2008. The endemic Mediterranean yelkouan shearwater Puffinus yelkouan: distribution, threats and a plea for more data. Oryx 42(2): 187-194. Capizzi, D., Baccetti, N. and Sposimo, P. 2010. Prioritizing rat eradication on islands by cost and effectiveness to protect nesting seabirds. Biological Conservation 143(7): 1716-1727. Carboneras, C., Jutglar, F. and Kirwan, G.M. 2014. Yelkouan Shearwater (Puffinus yelkouan). In: del Hoyo, J., Elliott, A., Sargatal, J., Christie, D.A. and de Juana, E. (eds.) 2014. Handbook of the Birds of the World Alive. Lynx Edicions, Barcelona. (retrieved from http://www.hbw.com/node/52574 on 16 January 2015). Derhé, M.A. 2012. Population assessment for the Yelkouan Shearwater Puffinus yelkouan. In: BirdLife International (ed.), Methodology for Bird Species Recovery Planning in the European Union. Final Report to the European Commission. BirdLife International for the European Commission, Cambridge, UK. Lebreton, J.D. 2000. Dinámica de poblaciones y conservación de aves marinas: el papel de los modelos matemáticos. 6th Mediterranean Symposium on Seabirds. Conference on Fisheries, Marine Productivity and Conservation of Seabirds. Benidorm, Spain. 11-15th October 2000. Book of abstracts 39. Louzao, M., Arcos, J.M., Laneria, K., Beldae, E., Guallartf, J., Sánchez, A., Giménez, M., Maestre, R. and Oro, D. 2011. ["Evidence of the incidental capture of the Balearic Shearwater at sea"]. Proceedings of the 6 CONGRESS of GIAM and the International workshop on petrels and shearwaters ecology at southern Europe. 34: 165-168. Oppel, S., Raine, A.F., Borg, J.J., Raine, H., Bonnaud, E., Bourgeois, K. and Breton, A.R. 2011. Is the Yelkouan shearwater Puffinus yelkouan threatened by low adult survival probabilities? Biological Conservation 144(9): 2255-2263. Oro, D., Aguilar, J.S., Igual, J.M. and Louzao, M. 2004. Modelling demography and extinction risk in the endangered Balearic shearwater. Biological Conservation 116: 93-102. Raine, H., Borg, J.J., Raine, A., Bariner, S. and Cardona, M.B. 2007. Light Pollution and Its Effect on Yelkouan Shearwaters in Malta; Causes and Solutions. Malta: Life Project Yelkouan Shearwater. BirdLife Malta. Snow, D.W. and Perrins, C.M. 1998. The Birds of the Western Palearctic vol. 1: Non-Passerines. Oxford University Press, Oxford.

Bibliography Sultana, J. and Borg, J.J. 2006. Population ecology and conservation of the Cory s Shearwater (Calonectris diomedea). Proceedings of the first symposium on the Mediterranean action plan for the conservation of marine and coastal birds - RAC/SPA, Tunis: 37-39. Tavecchia, G., Minguez, E., De Leon, A., Louzao, M. and Oro, D. 2008. Living close, doing differently: small-scale asynchrony in demography of two species of seabirds. Ecology 89: 77-85 Map (see overleaf)