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MAP Technical Reports Series No. 106 UNEP

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- 126 -<br />

Transplantation of mussels (Mytilus edulis) contaminated by okadaic acid (0A) from<br />

a more toxic environment in the northern part of the Swedish west-coast to a less toxic<br />

environment in the southern part showed a decrease in 0A content of 12 mg 0A/100 g mussel<br />

meat per day (Haamer et al., 1990). Transplantation of less toxic mussels from the south to the<br />

north did not show a rapid uptake of 0A. Toxic mussels from the north were reimmersed in two<br />

basins. One of them contained ordinary sea water, and to the other boiled baker's yeast was<br />

added. Decreases of 4-5 µg 0A/100 g mussel meat per day were observed. The 0A-data<br />

showed a more consistent behaviour when boiled yeast added. Without yeast, decreases<br />

alternated with increases.<br />

7.2.2.7 Methods of analysis for DSP<br />

The bioassay of all DSP components is based on the dose that provokes a fixed death<br />

time in mice injected intraperitoneally with a toxic residue extracted from shellfish with acetone<br />

(Yasumoto et al., 1984). The acetonic phase is evaporated and the residue resuspended in 4<br />

ml of 1% Tween 60. Aliquots of 1 ml of this solution are injected i.p. into 18-20 Swiss albino<br />

mice. This procedure is the official method in Japan and in several other countries. In France<br />

toxicity is expressed differently from the official Japanese biological test. In Italy, the method<br />

established by the Ministerial Decree dated 1.9.1990 (Ministero della Sanità, 1990c) is similar<br />

to the official method used in France (Marcaillon-Le Baut and Masselin, 1990). The mice were<br />

observed for 24 hr and positive tests consists in T < 5 hr. Other bioassay methods are: suckling<br />

mouse bioassay (Hamano et al., 1985), rat bioassay (Kat, 1983), Tetrahymena test (Shiraki et<br />

al., 1985).<br />

The fluorometric determination of okadaic acid and DTX-1 has been developed using<br />

HPLC (Lee et al., 1987). The bioassay and the HPLC method have not been studied<br />

collaboratively, and no attempts have been made to study the scientific parameters, such as<br />

precision, sensitivity and specificity. The intercalibration procedure is not appliable since at<br />

present only okadaic acid and DTX-1 as reference material for the DSP components are<br />

commercially available. A "second stage" analysis is the identification of okadaic acid and other<br />

DSP toxins through 1 H NMR spectroscopy of fractions positive to official mouse lethality test,<br />

obtained by repeated chromatographic separation (Fattorusso et al., 1992). Although it is a more<br />

laborious test than fluorimetric HPLC assay (Lee et al., 1987), which has a similar scope, it has<br />

two important advantages: it does not need any standard sample of the toxins, which may be<br />

difficult to purchase for toxins other than okadaic acid and DTX-1 (Krogh, 1989); only literature<br />

NMR data are required. In addition this method is not limited to known toxins, but can potentially<br />

work with new ones, also allowing their structural elucidation, provided a large enough quantity<br />

of toxic material can be obtained.<br />

7.2.2.8 Human intoxication: clinical toxicology<br />

Frequency of signs and symptoms of DSP in patients were as follows: diarrhoea<br />

(92%), nausea (80%), vomiting (79%), abdominal pain (53%), and chill (10%). The incubation<br />

period ranged from 30 min to several hours but seldom exceeded 12 hr. Around 70% of the<br />

patients developed symptoms within 4 hr. Suffering may last for 3 days in severe cases but<br />

leaves no after-effects (Yasumoto et al., 1978; Lucas, 1985). Thus no fatal case has ever been<br />

recorded. The minimum amount of DSP required to induce disease in adults has been<br />

estimated from analysis of left-over food to be 12 MU (Yasumoto et al., 1984). In Scandinavia<br />

mussels associated with the outbreak contained approximatively 17 MU per 100 g (Underdal et<br />

al., 1985). In an inventory of phytoplankton perturbation along the French coast in 1986 the higher<br />

DSP levels in shellfish were 10.6 MU/100 g (Belin and Berthomé, 1988).

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