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MAP Technical Reports Series No. 106 UNEP

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In contrast, it seems that the seabirds (gulls in particular) seem to be benefiting from<br />

the situation: when the benthic fish come to the surface gasping for oxygen before dying, flocks<br />

of gulls (Larus ridibundus and Larus argentatus) gather in the area. It is well known that the<br />

numbers of these species are growing because of their ability to adapt in an opportunist way to<br />

various forms of human activity (fishing, agriculture and landfills), causing damage to more<br />

"delicate" species, particularly during the breeding and migration seasons. The way in which they<br />

interfere with and even prey on the eggs and nestlings of species such as oyster catchers<br />

(Haematopus ostralegus), avocets (Recurvirostra avosetta) etc. which nest in areas adjoining<br />

or overlapping with those of the herring gull (L. argentatus) is in fact well known.<br />

6.2.3 Immature macrozoobenthic community along the coast of the Emilia- Romagna region<br />

The macrozoobenthic community in the northern Adriatic Sea, south of the Po river,<br />

along the coast of the Emilia-Romagna region, was sampled in 1985 (Crema et al., 1991). The<br />

sampling site was in the centre of a highly eutrophied area with greatly increased intensity and<br />

frequency of dystrophic events over recent decades. The sampled community differs from all<br />

those described in the same area in a period (1934-1936) (Vatova, 1949) previous to the current<br />

degree of eutrophication. Large abundances of species indicative of unstable bottoms, such as<br />

the bivalve Corbula gibba and the polychaete Lumbrineris latreilli were recorded.<br />

The recent biocenosis is characterized by a large abundance of Corbula gibba, a<br />

species typical of the transition zone between detrital and muddy bottoms. Its dominance is of<br />

particular interest. In fact, Corbula gibba is known to be a pioneer species in the recolonization<br />

of defaunated bottoms (Bonvicini Pagliai et al., 1985; Curini Galletti, 1987; Crema, 1989), and<br />

is prominent in subnormal zones in areas polluted or enriched by organic material (Ghirardelli<br />

and Pignatti, 1968; Pearson and Rosenberg, 1978; Bourcier et al., 1979; Russo, 1982).<br />

This bivalve was also dominant, in association with Lumbrineris latreilli, in the Gulf of<br />

Fos, subjected to extensive dredging, and it has been included in a stock of species typical of<br />

unstable bottoms (Salen Picard, 1981).<br />

Moreover, the community structural features indicate a state of immaturity, such as in<br />

early successional stage communities. The increased frequency of acute dystrophic events and<br />

consequent shortening of the time between consecutive disturbances is proposed as the cause<br />

of the modification of biocenosis, and its current structure and composition in the <strong>No</strong>rthern<br />

Adriatic Sea, and in eutrophicated coastal areas of the Mediterranean.<br />

6.2.4 Research in the laboratory and in the field on the resistance of bivalves to oxygen<br />

deficiency<br />

De Zwaan et al. (1992) carried out laboratory survival tests to determine the resistance<br />

of benthic organisms to oxygen deficiency. In sea water where oxygen levels were reduced by<br />

bubbling through nitrogen, he performed tests on a number of bivalves endemic to the <strong>No</strong>rth-<br />

West Adriatic such as: Chamelea gallina, Tapes philippinarum, Mytilus galloprovincialis and<br />

Schapharca inaequivalvis. The 50% survival times of the individuals used demonstrated that the<br />

most resistant is S. inaequivalvis with 19 days, followed in decreasing order by M.<br />

galloprovincialis with about 16 days, T. philippinarum with 12 and finally C. gallina with about 6<br />

days.

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