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MAP Technical Reports Series No. 106 UNEP

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- 124 -<br />

7.2.2.4 DSP occurrence in the Mediterranean sea<br />

In June 1989 the presence of Dinophysis fortii cells in hepatopancreas of mussels and<br />

of lipid soluble toxin of DSP type in mussel tissue collected in the coastal water of the Emilia-<br />

Romagna region (Boni et al., 1992) allowed to prove that the cause of certain cases of diarrhoea<br />

in consumers of molluscs was not due to bacteria or virus but to biointoxication by DSP. This<br />

phenomenon, brought to light by the Research Centre of Marine Biological Resources of<br />

Cesenatico (University of Bologna, Italy), has subsequently extended over the coastal areas of<br />

Marche, Abruzzo, Veneto and Friuli-Venezia Giulia. The existence of the enterotoxin in seafood<br />

was initially revealed by the McFarren et al. (1965) method (biological test for the research into<br />

fat-soluble algal biotoxins, according to the previsions of Italian Law) (Ministero della Sanità,<br />

1978). In the second stage the Yasumoto et al. method (1984) was used. Although coloured<br />

water and algae blooms have regularly been seen since 1975 in the areas of the Adriatic Sea<br />

off Emilia-Romagna (Viviani, 1981, 1983, 1988; Viviani et al., 1985), the appearance of molluscs<br />

toxic because of DSP in 1989 and 1990 was not preceded or accompanied by evident<br />

phenomena of this kind (Boni et al., 1992; Viviani et al., 1990).<br />

The toxicity of mussels was correlated, in 1989 and 1990, with the presence of D. fortii,<br />

D. sacculus, D. acuta, D. caudata, D. rotundata, D. tripos and species similar to D. acuminata<br />

in quantities of 2,000 cells/litre and even only 40 cells/litre (Viviani et al., 1990; Boni et al., 1992).<br />

These species of dinoflagellates had not previously given rise to mono-specific blooms, but their<br />

presence had been detected by the analysis of the phytoplankton carried out by the Cesenatico<br />

Centre since 1976. From the data on the presence of phytoplankton in the seawater off the coast<br />

of Emilia-Romagna (Table 23) and in the hepatopancreas of mussels (Mytilus galloprovincialis)<br />

it can be seen that there are many species of Dinophysis and that the toxic material is related<br />

to the following species: D. fortii is dominant in June and July, D. sacculus in August and<br />

September, D. fortii and D. caudata in October and <strong>No</strong>vember, D. tripos in December.<br />

Table 23<br />

Monthly distribution mean (cell/dm 3 ) of Dinophysis spp. along the<br />

Emilia-Romagna coast during 1989 (Boni et al., 1992; Viviani et al., 1990)<br />

Month D. acuminata D. caudata D. fortii D. sacculus D.sp. D. tripos<br />

June<br />

July<br />

August<br />

September<br />

October<br />

<strong>No</strong>vember<br />

December<br />

8<br />

0<br />

0<br />

0<br />

0<br />

3<br />

0<br />

0<br />

0<br />

0<br />

10<br />

124<br />

43<br />

6<br />

Also along French Mediterranean coast (Sete) in June 1989, during Dinophysis spp.<br />

blooms the presence of DSP toxins in mussels has been reported (Lassus et al., 1991). In<br />

addition few cases of poisoning due to ingestion of mussels contaminated by Dinophysis spp.<br />

were encountered in the region situated outside the Etang the Thau (Thau Lagoon) (Leveau et<br />

al., 1989).<br />

136<br />

130<br />

0<br />

90<br />

148<br />

89<br />

29<br />

16<br />

0<br />

640<br />

615<br />

80<br />

11<br />

6<br />

8<br />

80<br />

0<br />

90<br />

0<br />

6<br />

0<br />

32<br />

50<br />

0<br />

5<br />

48<br />

54<br />

63

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