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Tomasello, Di Maida, Calvo, Pirrotta, Borra & Procaccini                       Seagrass meadows at the extreme of environmental tolerance

         A 12                                        n.s.                      those found outside the lagoon. This situation could
                                                                               generate inbreeding among the confined P. oceanica
mm year–1    11                                                                shoots with genetic drift and possible selection of adapted
             10                                                                genotypes in the northern basin of the lagoon. The lower
                               Récif  Plateau        Nubia  Marsala Favignana  growth rate in the lagoon as inferred from lepidochrono-
              9                                                                logical data and the lack of flowering are indicative of
              8                                Site                            persistent stressful conditions.

             7 **                                    n.s.                         The Atolls population exhibits a lower number of
                                                                               alleles, lower percent of polymorphic loci, lower clonal
              6                                                                diversity and higher heterozygosity excess relative to the
              5                                                                other sites included in the present analysis. Different rea-
                                                                               sons can account for the high heterozygosity. First, in the
                      Atollis                                                  literature high heterozygosity has been positively corre-
                                                                               lated with fitness, particularly when organisms live in
         B9                                                                    unfavorable environmental conditions. This has been
                                                                               demonstrated experimentally in mice for functional traits
             8                                                                 represented by allozymes (Teska et al. 1990). In theory it
                                                                               should not apply if the markers utilized are truly neutral,
n year–1                                                                       which is generally assumed for microsatellites (Hansson &
                                                                               Westerberg 2002). Nevertheless, it has been demonstrated
           7                                                                   that microsatellites have a range of different functions
                                                                               within the genome (Li et al. 2002) and we cannot exclude
                  ***                                                          the possibility that some loci utilized here show patterns
                                                                               not consistent with neutrality (see Oetjen & Reusch 2007
           6                   Récif  Plateau        Nubia  Marsala Favignana  for Zostera marina). Secondly, excess of heterozygosity in
                  Atollis                                                      neutral markers can also derive from the combined effect
                                                                               of linkage disequilibrium and partial inbreeding (Hansson
                                               Site                            & Westerberg 2002), a scenario which could easily apply
                                                                               to the Stagnone populations. Nevertheless, our results do
Fig. 4. Estimate of mean rhizome elongation (A) and annual leaf for-           not completely support this latter option. All populations
mation (B). Estimate of mean rhizome elongation have been retro-               analysed here, in fact, have a negative Fis value, but the
spectively corrected, as if all shoots have been sampled with same             value is consistently lower in the Atolls population than
age, corresponding to the grand mean (8.1 years). Significance: ***             in the others, showing lower inbreeding in the more
P < 0.001; ** P = 0.001–0.01; ns, P > 0.05. Bar indicates standard             confined locality. The highest number of loci showing
error.                                                                         potential linkage, instead, is present at the Atolls site.

Stagnone di Marsala coastal lagoon. Each atoll is com-                            In general, species inhabiting temporally variable or
posed of multiple genotypes, which falsifies the hypothesis                     spatially heterogeneous environments exhibited higher
of their monoclonal structure. Nonetheless, the atolls
show characteristics of genetic isolation, namely the exis-
tence of alleles and genotypes which are distinct from

Table 4. Average frequency of meadow (FF, flowering years per year), shoot flowering probability (Pf, inflorescence Æ shoot)1 Æ year)1), and flow-
ering intensity (inflorescences Æ shoot)1, calculated from meadows FI means) for the six sampling sites.

           number of
           shoots

               present previous number of time horizon                                                            Time
site study study total shoots (FF and Pf) FF ± SE (nstation) Pf (nstation)                                        horizon (FI) FI ± SE (nstation)

Atolls      40                  99     139                 84–04  0.00 (ns = 1)          0.0000(ns = 1)           92–00    0.00(ns = 1)
Re´ cif     40                  53       93                89–04  0.188(ns = 1)          0.0051(ns = 1)           94–99    0.017 ± 0.002(ns = 1)
Plateau     38                  11       49                92–04  0.077(ns = 1)          0.0022(ns = 1)                    –
Nubia       42                 202                         92–04  0.282 ± 0.082(ns = 2)  0.0087 ± 0.0008(ns = 2)        –
Marsala     41                 167     244                 88–04  0.249 ± 0.018(ns = 2)  0.0092 ± 0.0041(ns = 2)  95–99    0.028 ± 0.015(ns = 2)
Favignana   42                 234     208                 80–04  0.217 ± 0.063(ns = 2)  0.0108 ± 0.0016(ns = 2)  94–99    0.013 ± 0.005(ns = 2)
total      243                 766     276                 80–04  0.196 ± 0.036(ns = 9)  0.0072 ± 0.0015(ns = 9)  85–99    0.032 ± 0.015(ns = 2)
                                      1009                                                                        85–00    0.026 ± 0.007(ns = 8)

Marine Ecology 30 (2009) 288–300 ª 2009 Blackwell Verlag GmbH                                                                                      295
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