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L. Campanella et al. / Environmental Pollution 111 (2001) 117±126 123
The mean metal concentrations in biota and seawater rather than in rhizomes is a well-established pattern,
are shown in Table 8, where only data from the four our results matching those of many previous studies
clean sites are averaged. From these data it results that (Sanchiz et al., 1990; Warnau et al., 1995; Schlacher-
accumulation ratios of the ®ve metals dier both in Hoenlinger and Schlacher, 1998a).
macrophytes and in molluscs. In P. oceanica metal
concentrations decrease in the following order: In the present study, the opposite behaviour was
Zn>Cu>Cd>Pb>Cr while in P. pavonica the observed in the case of Cr and Pb. This ®nding matches
sequence is Zn>Cu>Pb>Cr>Cd. As for molluscs, those of Warnau et al. (1995) and Schlacher-Hoenlinger
the following sequences were observed: Zn>Cu>Cd> and Schlacher (1998a). However, Sanchiz et al. (1990)
Cr5Pb in M. turbinata; Zn>Cd>Cu>Cr>Pb in P. described the sequence old leaves>rhizomes>young
caerulea. leaves, while Catsiki and Panayotidis (1993) reported
somewhat erratic results, with inversions of the accu-
As far as net accumulation is concerned, P. caerulea mulation ratio between leaves and rhizomes depending
turned out to be the strongest accumulator for Cd, P. on the sampling area.
pavonica for Cr and Pb, M. turbinata, P. oceanica and P.
pavonica for Cu, P. oceanica for Zn. Very high con- The almost constant Cu content observed in all plant
centration factors (1.0Â104Ä 3.4Â104) can be calculated tissues (as in Warnau et al., 1995), can be supposed to
in these cases with reference to soluble metal concentra- arise from a certain regulation capability of the phaner-
tions in ambient seawater. Anyway it must be kept in ogam. Again, con¯icting results can be found in the lit-
mind that in the studied organisms the actual uptake erature (Catsiki and Panayotidis, 1993; Schlacher-
mechanisms are probably rather complicated because Hoenlinger and Schlacher, 1998a), so that further stu-
their exposure to trace elements is not limited to soluble dies are needed to fully elucidate this point.
metals in the aquatic medium. The metal uptake from
food, in the case of molluscs, and from sediments In leaf material Cd, Cr, Pb and Zn concentrations
(through the roots) in the case of seagrasses, cannot be decrease in the following order: leaf tip>whole leaf
ignored. As both mollusc species here considered are >leaf basal tissue. This trend is consistent with the
herbivorous, it can be supposed that the metals accumu- observation that the seagrass leaves grow by formation
lated in the algae on which they graze fairly aect their of new tissue at the base. Therefore, the tip becomes the
overall uptake. older part of the leaf, hence the tissue with a longer
exposure to metal loads in the ambient habitat.
4. Discussion
As regards absolute metal contents, levels recorded in
The picture of bioavailable metal loads in the dierent this study at clean stations, generally fall in the range of
sites of the experimental area provided by the four the lowest values available in the literature.
selected organisms is rather univocal. An overall trend
of increased metal concentrations in station 5 is clear, In detail, our data concerning the leaves of Posidonia
especially for Cd, Pb and Zn. Moreover, many correla- oceanica are well below those previously reported in the
tions between metal contents were observed in the four case of Cr and Pb, while for Cu and Zn the results we
species. obtained are only slightly lower than the mean values
described elsewhere (Table 9). As for Cd, our mean
The results of the study on metal distribution in the level is lower than those previously reported, with the
tissues of Posidonia oceanica are particularly mean- exception of the surprisingly small one observed by
ingful. In fact the dierent behaviour of the metal cou- Schlacher-Hoenlinger and Schlacher (1998a) in speci-
ple Cd±Zn on the one hand, and Cr±Pb on the other, mens collected at Ischia (Bay of Naples, Italy). In Padina
suggests dierent uptake and distribution routes for pavonica the observed levels of Cd and Cr are generally
these elements. The highest concentration of Cd and Zn lower than those previously reported, while Pb, Cu and
in leaves versus rhizomes leads to the hypothesis of a Zn contents are higher (Catsiki et al., 1991; Tariq et al.,
preferential uptake of these elements from water to the 1991; Schlacher-Hoenlinger and Schlacher, 1998b).
photosynthetic tissue. Warnau et al. (1996) reported
that Cd and Zn were linearly accumulated from ambient Very few data are currently available on trace metals
water by seagrass shoots during a 15-day experiment. concentrations in the gastropod molluscs selected in the
However, in a ®eld study on a contaminated area, present study. However, our values, except for Cd, are
Malea et al. (1994) described a signi®cant positive cor- lower than those reported by other authors (Ozretic et
relation between Cd concentrations in leaves and those al., 1990; Nicolaidou, 1994).
in sediments. Therefore, an ecient distribution from
roots to green tissues cannot be excluded. Anyway, In the light of the foregoing remarks, the metal con-
the preferential accumulation of Cd and Zn in leaves centrations in the organisms collected at the `clean' sta-
tions may be considered as useful background levels to
which to refer for intraspeci®c comparison within the
Mediterranean area. It must be noted that in the pres-
ent context the notion of `background levels' has a
somewhat relative meaning, as local geochemical or
hydrodynamic conditions may always shift `natural'