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1642                                                                            L. Ruffino et al.


                                                          coexistence is likely to provide important clues to
                   (1985)  (unpublished  (2005),  2008)   conservation and restoration priorities on other rat-
                   Vidal               Pascal  (2006,  (1997)  invaded islands worldwide. Here we hypothesize that
                                                          the long-term persistence of these seabirds at the scale
                   (1985),      (1995)  and  al.  et  al.  et  of the Western Mediterranean Basin may have been
                                                          facilitated by the various biogeographical contexts of
               References  Cheylan  CEEP-Marseille  report)  Thibault  Lorvelec  Pascal  Thibault  Mediterranean islands, providing intra-island refuge
                                                          areas where interactions with introduced rats may be
                                                          limited. Rat densities on islands and their fluctuations
                                                          over time are known to be major factors in seabird
                                                          vulnerability within breeding sites (e.g., Igual et al.
               populations  from  increased  chicks/  after  75%  nearly  in  failure  increased  after  Gargalu:  Giraglia:  2006), with seabird productivity increasing when rat
                                                          densities are low (Quillfeldt et al. 2008). This
                                                          intriguing coexistence, along with evidence of rat
               seabird  fluctuated  year  success  fledged  and  65%  for  breeding  years  success  83%  to  on success  on  rats),  rats)  (without  impact on Mediterranean seabirds, also raises new
                                                          questions on the mechanisms and the intensity by
               on  impact  to  25%  to  control  responsible  of  44%  eradication  (with  which invasive rats really affect seabirds, and on their
                                                          ability to drive them to extinction. More work is also
               Effects  Rat  year  Breeding  from  adult  rat  Rats  85%  certain  Breeding  from  Breeding  3%  73%  needed to clarify the complex relationships linking
                                                          factors likely to influence rat population densities (i.e.,
                                                          diversity of available resources, presence of other
                                                          alien predators or competitors on islands), foraging
               affected  chicks  and  mainly              strategy of rats and rat impact on seabird populations.
                                                          As claimed by Towns et al. (2006), we suggest that the
               Stage  Eggs      Chicks  ?    ?            role of rats in seabird population decline should be
                                                          carefully evaluated relative to that of other factors and
                                                          caution should be used in attributing any seabird
               Species  Y  C    C      C     C            breeding failures, and local or global extinctions to
                                                          rats. The better we understand both patterns and
                                                          mechanisms causing decline, the better we can focus
                                                          our efforts on the most effective measures to mitigate
                                                          threats.
                                             Giraglia     Acknowledgments  We would like to thank all the people

                   and  Porquerolles  and    and          who provided data, contacts, unpublished reports, and other
                                                          information: H. Azafzaf, J. Borg, G. Brundu, F. Corbi, C. Cure ´,
                                                          J. Fric, J. M. Igual, M. Louzao, A. Martinez Abrain, B. Massa,
               Island  Port-Cros  Pomegues  `  Ratonneau  Lavezzu  Lavezzu  Gargalu  F. Me ´dail, R. Moulia, S. Pasta, J. D. Vigne. We also thank D.
                                                          Drake and T. Hunt for inviting us to write this paper, M.
                                                          Sweetko for improving the English, Y. Delettre (CNRS, UMR
                                                          6553 Ecobio, Rennes), and two anonymous referees for helpful
                                                          comments on earlier drafts of the manuscript. Funds were
                       Marseilles  Corsica   Corsica      provided by a PhD fellowship granted by the ‘‘Ecole Doctorale
                                                          des Sciences de l’Environnement’’ to L. R. and by a post-
                                                          doctoral fellowship from the ANR (‘‘ALIENS’’ project) to K. B.

            continued  Area  `  Hyeres  Frioul,  Lavezzi,  Northern  Appendix 1



            5
            Table  Country  France                        See Table 6.



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