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270    F. Espinosa et al.

            TABLE 3 PERMANOVA analysis of the effect of substrate and protection on the size (measured on the longitudinal axis) structure of P.
            ferruginea populations. The matrix used was the same as for the MDS analysis (Fig. 3).

            Source                     Df           SS                 MS               Pseudo-F          P
            Substrate                   1             421.56            421.56          0.36              0.786
            Protection                  1            3,516.30          3,516.30         2.96              0.042
            Substrate×protection        1              29.90             29.90          0.03              0.994
            Residual                   17           20,164             1,186.10
            Total                      20           24,111



                                                                               FIG. 3 MDS ordination of populations
                                                                               (only those with .10 individuals) of
                                                                               P. ferruginea based on the number of
                                                                               individuals per size class. Groups of
                                                                               samples determined by the SIMPROF test
                                                                               are enclosed by ellipses. Populations
                                                                               include six from this study (Table 2) and
                                                                               15 from published data (Table 4).
                                                                               Designation as unprotected (circles) or
                                                                               protected (triangles) indicates the
                                                                               likelihood or not, respectively, of
                                                                               exploitation, based on accessibility. ANP,
                                                                               artificial substrate, non-protected; AP,
                                                                               artificial substrate, protected; NNP,
                                                                               natural substrate, non-protected; NP,
                                                                               natural substrate, protected. Arrows
                                                                               indicate artificial substrates.


            threatened status of the species (Paracuellos et al., 2003;  there has also been a noticeable decline on these islands,
            Bazairi et al., 2004; Guerra-García et al., 2004; Espinosa,  with a large decrease in mean density at several sites from
                                                                                      −1
            2006; Cristo & Caronni, 2008; Espinosa et al., 2009a,b, and  1985 to 2009: 0.933 to 0.02 m at Tizzano (Laborel-Deguen
            references therein), mainly a result of human pressure, these  & Laborel, 1990; present study) and 2.334 to 0.13 m −1  at
            studies were at a local or regional scale. The information  Gáleria (Laborel-Deguen & Laborel, 1991b; present study;
            summarized here demonstrates that the range of this  Fig. 4). Exploitation in Corsica during summer has been
            threatened mollusc has contracted severely and that the  reported by Laborel-Deguen & Laborel (1990, 1991b).
            remaining populations are scarce and generally sparse.  In Tunisia P. ferruginea is restricted to the north-
               The species has not been reported from the Italian  eastern shores, as also reported by Tlig-Zouari et al. (2010).
            mainland since the 1980s, when it was recorded in low num-  The largest and most structured population (i.e. presence
            bers at a few locations in Tuscany (Curini-Galletti, 1979;  of different size classes) is on the Zembra archipelago,
            Terreni, 1981; Biagi & Poli, 1986) and one location in Liguria  although Tlig-Zouari et al. (2010) reported lower densities
            (Porcheddu & Milella, 1991). However, we did not find the  at Zembra than at Cap Bon. However, on Zembra they
            species at any of these locations. The situation on the Italian  surveyed at a location with the lowest densities, which is
            islands of Egadi, Sicily and Pantelleria is also critical.  probably not representative of the archipelago. The species
            Giaccone & Sortino (1974) reported P. ferruginea on the  shows great variability in recruitment (Guallart et al., 2006;
            Egadi islands with a relative abundance of II, within a range  Rivera-Ingraham, 2010) and the high densities found at
            from I (rare) to V (abundant), but it is now extremely scarce,  some sites at Cap Bon by Tlig-Zouari et al. (2010) could be a
            having also declined in density. Giaccone et al. (1973)  result of good recruitment from the Zembra population
            reported the species in a general phytobenthos study at  during 2006.
            Pantelleria but we detected only one small specimen there,  Many authors have demonstrated the influence of
            despite the focus on this species. There are some specimens  exploitation on the mean size and presence of large repro-
            from Palermo, Sicily, in Locard’s 1892 collection at the  ductive individual molluscs (Keough et al., 1993; Branch &
            Muséum national d’Histoire naturelle, Paris, but the species  Odendaal, 2003). Patella ferruginea is used as food and
            no longer occurs on the island.                    fishing bait and as a collector’s item (Laborel-Deguen &
               The Corsican and Sardinian populations were greater in  Laborel, 1991a, b; Templado & Moreno, 1997; Ramos, 1998),
            density than those on the Egadi islands and Pantelleria but  the latter confirmed by our observations of shells being sold


                                                                               © 2013 Fauna & Flora International, Oryx, 48(2), 266–275

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