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MAP Technical Reports Series No. 106 UNEP

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- 71 -<br />

Some of the coastal lagoons in the Languedoc-Rossignol Region are also affected by<br />

periodic events of eutrophication (Ménesguen, 1990). Lieutaud et al. (1991) attribute the gradual<br />

trophic deterioration of eight lagoons along the shoreline of Montpellier (from the Or to the Ingril<br />

lagoons) to the increased input of nutrients of urban and agricultural origin.<br />

- Eastern zone between the Rhône delta and the Italian border. This zone receives the<br />

effluents from large towns and cities (Marseilles, Toulons, Cannes and Nice) and from important<br />

industrial areas (Region of Fos). There are generally no eutrophication phenomena in the open<br />

sea waters because of the westward drift of oligotrophic waters carried by the Liguro-Provinçal<br />

Current (Sournia et al., 1990). Events of algal blooms are mainly limited to ports and coastal<br />

waters near the points of urban and industrial effluent discharges. The same applies to the Berre<br />

and Vaine Lagoons, where Kim and Travers (1986) report high nutrient values and the<br />

development of massive algal blooms. Bellan (1972) discusses the gradual deterioration of the<br />

Berre and Vaine lagoon due to heavy pressure from the human population, which has caused<br />

profound modifications in the animal and vegetable communities typical of these ecosystems.<br />

Vitello and Keller (1991) reach the same conclusions from their studies on the meiobentos of<br />

the Berre lagoon.<br />

- Corsica. This island, with few lagoons (Diana and Urbino) and with a fairly high level of<br />

hydrodynamism along its coasts, is only marginally affected by the urban effluents from the cities<br />

of Bastia and Ajaccio, and by the small amounts of industrial effluents discharged.<br />

Eutrophication phenomena are of little significance and very occasional off Corsica.<br />

As to nuisance species it appears that the numbers of toxic flagellates present in<br />

French seas have increased over time. Until 1982 only Gyrodinium aureolum was present, while<br />

the Dinophysis species appeared in 1983 gradually becoming dominant. Alexandrium minutum<br />

was reported for the first time in 1988 (Belin et al., 1989). Dinophysis is present off the South<br />

coast of France, where it is thought to have made its first appearance in 1987 (Leveau et al.,<br />

1989; Lassus et al., 1991).<br />

Routine analyses performed in areas affected by the presence of toxic flagellates have<br />

highlighted three important facts:<br />

a) their presence cannot be correlated with and does not depend on the inputs of<br />

nutrients resulting from human activities;<br />

b) in the areas where these organisms are present there is no alteration at the level<br />

of grazing due to inputs of pollutants (Leveau et al., 1989);<br />

c) their presence even at low concentrations (a few individuals/litre) and in absence<br />

of real blooms may be unsafe to human health.<br />

It must be noted that anoxia in French coastal waters has never reached the levels of<br />

the Skagerrat (Rosenberg, 1985) or the northern Adriatic (Rinaldi et al., 1993). Shortages of<br />

oxygen in the waters near the sea-bed after algal blooms were reported in the Bay of Vilaine in<br />

July 1984 (Marceron, 1987), but there were no serious consequences.<br />

5.2.3 The Coasts of Italy<br />

General. Manifestations of eutrophication occurring in the Italian seas depend on the<br />

hydrology, hydrodynamics and morphology of the areas concerned. In the Ligurian Sea, the<br />

Tyrrhenian Sea and the southern Adriatic, the phenomena are episodic and generally not

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