Assessment of the hydrolysis process for the determination of okadaic acid-group toxin ester: presence of okadaic acid 7-O-acyl-ester derivates in Spanish shellfish.

The contamination of different types of shellfish by okadaic acid (OA)-group toxin esters is an important problem that presents serious risk for human health. During previous investigations carried out in our laboratory by liquid chromatography coupled with tandem mass spectrometry (LC/MS/MS), the occurrence of a high percentage of esters in relation to the total OA equivalents has been observed in several shellfish species. The determination of these kinds of toxins using LC/MS or other chemical methods requires a hydrolysis step in order to convert the sterified compounds into the parent toxins, OA, dinophysistoxins-1 (DTX-1) and dinophysistoxins-2 (DTX-2). Most of the hydrolysis procedures are based on an alkaline hydrolysis reaction. However, despite hydrolysis being a critical step within the analysis, it has not been studied in depth up to now. The present paper reports the results obtained after evaluating the hydrolysis process of an esterified form of OA by using a standard of 7-O-acyl ester with palmitoyl as the fatty acid (palOA). Investigations were focused on checking the effectiveness of the hydrolysis for palOA using methanol as solvent standard and matrices matched standards. From the results obtained, no matrix influence on the hydrolysis process was observed and the quantity of palOA converted into OA was always above 80%. The analyses of different Spanish shellfish samples showed percentages of palOA in relation to the total OA esters ranging from 27% to 90%, depending on the shellfish specie.

Lipophilic toxin profile in Galicia (Spain): 2005 toxic episode.

By the end of 2005, a toxic episode of phytoplankton origin in bivalve shellfish led to the closing down of several shellfish production areas in Galicia (northwestern region of Spain). During this time, different kinds of shellfish were collected and analysed by LC-MS/MS to search for the following lipophilic toxins: okadaic acid (OA), dinophysistoxins (DTXs), pectenotoxins (PTXs), azaspiracids (AZAs) and spirolides. Samples were analysed before alkaline hydrolysis in order to investigate the presence of free OA and DTXs, AZAs, PTXs and spirolides, and after alkaline hydrolysis to detect OA and DTXs esters. All of the samples were found to be contaminated with OA and/or DTX-2, as well as esterified forms of these diarrhetic shellfish poison (DSP) toxins, at levels around and above European regulatory limit (160 microg of okadaic acid equivalents/kg). The analyses of mussels and razor clam also revealed the presence of 13-desmethyl spirolide C (SPX-1) at levels below 31 microg/kg. Likewise, in many of the samples different levels of pectenotoxin-2 secoacid (PTX-2sa) were detected. DSP toxin esters represent practically the 100% of the total OA equivalents for scallops, clams, razor clams and cockles.

Influence of the sample toxic profile on the suitability of a high performance liquid chromatography method for official paralytic shellfish toxins control.

An HPLC-FLD method, involving pre-chromatographic oxidation of the PSP toxins with hydrogen peroxide and periodate, has been AOAC validated through a collaborative trial and adopted as AOAC Official Method. This method could be a candidate for replacing the mouse bioassay (MBA) for the Official Control of PSP toxins at European level, once accepted by the legislation. An interlaboratory exercise has been organized by the CRLMB to evaluate its "fitness for purpose" for the Official Control of PSP toxins in the EU laboratories. Eighteen EU laboratories took part in the study and had to analyze six bivalve mollusc samples with several PSP toxic profiles. The performance of the participant laboratories in the application of this method was compared with that obtained at the collaborative trial. Information on problems/drawbacks encountered by participants in the application of this method was also sought. The HPLC validated method is only applicable for Official PSP Control for certain samples. This depends on sample PSP toxic profile. Results obtained for samples where only GTX2,3 and STX were present were satisfactory and in agreement with MBA results. Results obtained for a sample with a toxic profile dominated by GTX6 and suspected to contain also C1,2 and C3,4 were not satisfactory. GTX5 and dc-STX could be quantified, although the results achieved (total toxicity) were lower than those obtained by MBA. It can be also useful as a screening method, complementary to MBA, helping in the reduction of the animals used. However, the lack of several PSP standards, the fact that the method is not validated for all the PSP toxins, and several drawbacks found in its application are a handicap to fully implement it for Official PSP Control as a viable replacement for bioassay.

First evidence of spirolides in Spanish shellfish.

During the months of November and December 2005, a harmful algal bloom in the northwestern region of Spain caused the accumulation of different algal toxins in several types of shellfish. Many of the shellfish were contaminated at levels above European regulatory limit, presenting serious risks for human health. The analysis of mussels sampled in the affected areas to search for lipophilic toxins, using liquid chromatography tandem mass spectrometry (LC-MS/MS), showed the presence of free okadaic acid (OA) and dinophysistoxin-2 (DTX-2) as well as esters of these toxins. The results also revealed the presence of minor amounts of 13-desmethyl spirolide C (SPX-1) in the analysed samples, although this toxin has never been reported before in Spain. The combination of different MS modes of operation, just as enhanced MS (EMS) and MS(3) experiments, allowed to confirm the first occurrence of spirolides in Spanish shellfish.