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2010).  Three of those five  species, Pilumnopeus vauquelini, Pilumnus minutus  and
                   Halimede tyche  are likely to have entered the Mediterranean via the Suez  canal,
                   while two species (Glabropilumnus laevis,  Actumnus globulus) probably did  so
                   through shipping activity (Galil et al., 2006).

                   Gonioinfradens paucidentatus
                   Gonioinfradens paucidentatus  (A. Milne Edwards, 1861) is a portunid crab with a
                   wide Indo-Pacific distribution: (Spiridonov and Neumann, 2008; Poupin, 1994; Apel
                   and  Spiridonov, 1998; Davie, 1998; Naderloo and  Sari, 2007)  (Fig. 24). It occurs
                   mainly on hard substrate from shallow subdital waters to 100 m of depth and
                   reaches a carapace length of 52.5 mm (Poupin, 1994).

























                   Figure 24. Gonioinfradens paucidentatus
                   (http://decapoda.free.fr/illustration.php?n=6andsp=156)

                   The first record for the Mediterranean Sea of the  Red Sea/Indo-Pacific portunid
                   Gonioinfradens  paucidentatus  (red swimming crab)  was reported in  Rodos Island
                   (southeastern Aegean Sea) is given, while  possible introduction vectors of the
                   species in the area are discussed (Corsini-Foca et al., 2010).
                          The following alien crabs have sporadically been found in many and various
                   areas of the Mediterranean basin: Myra subgranulata, Herbstia condyliata, Leucosia
                   signata, Xanthias lamarckii, Macrophthalmus graeffei, Ixa monody, Atergatis roseus,
                   Hyastenus hilgendorfi,  Coleusia signata,  Portunus segnis,  Thalamita poissonii,
                   Eucrate crenata,  Halimede tyche,  Atergatis roseus,  Micippa thalia,  Charybdis
                   (Charybdis) hellerii,  Carupa tenuipes,  Matuta victor,  Sirpus monodi,  Macropodia
                   tenuirostris.
                          Management practices with regard to the occurrence of ‘new’ species will
                   require comprehensive evaluation of changing habitat conditions and will depend on
                   the individual case. They could range from complete eradication to toleration and
                   consideration of the ‘new’ species as an enrichment of the local biodiversity as a
                   means to facilitate ecosystem restoration  or to maintain ecosystem function  as
                   native communities re-assemble and establish under a new climate regime.
                          A large number  of alien crabs have  entered and established in the
                   Mediterranean Sea,  rendering specific measures necessary for each introduction
                   pathway.  However a more integrated and comprehensive  approach to the
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