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Tetrodotoxin (TTX) is a potent neurotoxin causing human intoxications from contaminated seafood worldwide and is of emerging concern in Europe. Shellfish have been shown to contain varying TTX concentrations globally, with concentrations typically higher in Pacific oysters Crassostrea gigas in Europe. Despite many decades of research, the source of TTX remains unknown, with bacterial or algal origins having been suggested. The aim of this study was to identify potential source organisms causing TTX contamination in Pacific oysters in French coastal waters, using three different techniques. Oysters were deployed in cages from April to September 2021 in an estuary where TTX was previously detected. Microscopic analyses of water samples were used to investigate potential microalgal blooms present prior or during the peak in TTX. Differences in the bacterial communities from oyster digestive glands (DG) and remaining flesh were explored using metabarcoding, and lastly, droplet digital PCR assays were developed to investigate the presence of Cephalothrix sp., one European TTX-bearing species in the DG of toxic C. gigas. Oysters analysed by liquid chromatography-tandem mass spectrometry contained quantifiable levels of TTX over a three-week period (24 June-15 July 2021), with concentrations decreasing in the DG from 424 μg/kg for the first detection to 101 μg/kg (equivalent to 74 to 17 μg/kg of total flesh), and trace levels being detected until August 13, 2021. These concentrations are the first report of the European TTX guidance levels being exceeded in French shellfish. Microscopy revealed that some microalgae bloomed during the TTX peak, (e.g., Chaetoceros spp., reaching 40,000 cells/L). Prokaryotic metabarcoding showed increases in abundance of Rubritaleaceae (genus Persicirhabdus) and Neolyngbya, before and during the TTX peak. Both phyla have previously been described as possible TTX-producers and should be investigated further. Droplet digital PCR analyses were negative for the targeted TTX-bearing genus Cephalothrix., Competing Interests: Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper., (Copyright © 2024 Elsevier Ltd. All rights reserved.)

Dinoflagellates of the genus Dinophysis produce okadaic acid (OA) and analogues. Cultures of a strain of Dinophysis acuta isolated from the Galician Rías contained high levels of pectenotoxins but little OA. Isomeric forms of the latter were suspected as the concentration of OA increased after alkaline hydrolysis. High resolution mass spectra of candidate compounds suggest the presence of an OA-C9-diol ester, reported for the first time in Dinophysis acuta., (Copyright © 2018 Elsevier Ltd. All rights reserved.)

Algal toxins may accumulate in fish and shellfish and thus cause poisoning in consumers of seafood. Such toxins and the algae producing them are regularly surveyed in many countries, including Europe, North America, Japan and others. However, very little is known regards the occurrence of such algae and their toxins in most African countries. This paper reports on a survey of phytoplankton and algal toxins in Nigerian coastal waters. Seawater samples were obtained from four sites for phytoplankton identification, on three occasions between the middle of October 2014 and the end of February 2015 (Bar Beach and Lekki in Lagos State, Port Harcourt in Rivers State and Uyo in Akwa Ibom State). The phytoplankton community was generally dominated by diatoms and cyanobacteria; however several species of dinoflagellates were also identified: Dinophysis caudata, Lingulodinium polyedrum and two benthic species of Prorocentrum. Passive samplers (containing Diaion(®) HP-20 resin) were deployed for several 1-week periods on the same four sites to obtain profiles of algal toxins present in the seawater. Quantifiable amounts of okadaic acid (OA) and pectenotoxin 2 (PTX2), as well as traces of dinophysistoxin 1 (DTX1) were detected at several sites. Highest concentrations (60 ng OA g(-1) HP-20 resin) were found at Lekki and Bar Beach stations, which also had the highest salinities. Non-targeted analysis using full-scan high resolution mass spectrometry showed that algal metabolites differed from site to site and for different sampling occasions. Screening against a marine natural products database indicated the potential presence of cyanobacterial compounds in the water column, which was also consistent with phytoplankton analysis. During this study, the occurrence of the marine dinoflagellate toxins OA and PTX2 has been demonstrated in coastal waters of Nigeria, despite unfavourable environmental conditions, with regards to the low salinities measured. Hence shellfish samples should be monitored in future to assess the risk for public health through accumulation of such toxins in seafood., (Copyright © 2016 Elsevier Ltd. All rights reserved.)

The neurotoxin β-N-methylamino-l-alanine (BMAA) is naturally present in some microalgal species in the marine environment. The accumulation of BMAA has widely been observed in filter-feeding bivalves that are known to consume primary producers constituting the base of complex aquatic food webs. This study was performed to assess the occurrence of BMAA and isomers in mollusks collected from nine representative shellfish production areas located on the three French coasts (Channel, Atlantic and Mediterranean sites). The use of a highly selective and sensitive HILIC-MS/MS method, with D5DAB as internal standard, revealed the systematic detection of BMAA and DAB, in concentrations ranging from 0.20 to 6.7 μg g(-1) dry weight of digestive gland tissues of mollusks. While we detected BMAA in four strains of diatoms in a previous study, here BMAA was only detected in one diatom species previously not investigated out of the 23 microalgal species examined (belonging to seven classes). The concentrations of BMAA and DAB in mussels and oysters were similar at different sampling locations and despite the high diversity of phytoplankton populations that mollusks feed on at these locations. Only small variations of BMAA and DAB levels were observed and these were not correlated to any of the phytoplankton species reported. Therefore, extensive research should be performed on both origin and metabolism of BMAA in shellfish. The levels observed in this study are similar to those found in other studies in France or elsewhere. A previous study had related such levels to a cluster of Amyotrophic Lateral Sclerosis in the South of France; hence the widespread occurrence of BMAA in shellfish from all coasts in France found in this study suggests the need for further epidemiological and toxicological studies to establish the levels that are relevant for a link between the consumption of BMAA-containing foodstuffs and neurodegenerative diseases., (Copyright © 2015 Elsevier Ltd. All rights reserved.)

Marine biotoxins are algal metabolites that can accumulate in fish or shellfish and render these foodstuffs unfit for human consumption. These toxins, released into seawater during algal occurrences, can be monitored through passive sampling. Acetone, methanol and isopropanol were evaluated for their efficiency in extracting toxins from algal biomass. Isopropanol was chosen for further experiments thanks to a slightly higher recovery and no artifact formation. Comparison of Oasis HLB, Strata-X, BondElut C18 and HP-20 sorbent materials in SPE-mode led to the choice of Oasis HLB, HP-20 and Strata-X. These three sorbents were separately exposed as passive samplers for 24 h to seawater spiked with algal extracts containing known amounts of okadaic acid (OA), azaspiracids (AZAs), pinnatoxin-G (PnTX-G), 13-desmethyl spirolide-C (SPX1) and palytoxins (PlTXs). Low density polyethylene (LDPE) and silicone rubber (PDMS) strips were tested in parallel on similar mixtures of spiked natural seawater for 24 h. These strips gave significantly lower recoveries than the polymeric sorbents. Irrespective of the toxin group, the adsorption rate of toxins on HP-20 was slower than on Oasis HLB and Strata-X. However, HP-20 and Strata-X gave somewhat higher recoveries after 24 h exposure. Irrespective of the sorbent tested, recoveries were generally highest for cyclic imines and OA group toxins, slightly lower for AZAs, and the lowest for palytoxins. Trials in re-circulated closed tanks with mussels exposed to Vulcanodinium rugosum or Prorocentrum lima allowed for further evaluation of passive samplers. In these experiments with different sorbent materials competing for toxins in the same container, Strata-X accumulated toxins faster than Oasis HLB, and HP-20, and to higher levels. The deployment of these three sorbents at Ingril French Mediterranean lagoon to detect PnTX-G in the water column showed accumulation of higher levels on HP-20 and Oasis HLB compared to Strata-X. This study has significantly extended the range of sorbents for passive sampling of marine toxins. In particular, sorbents were included that had previously been evaluated for polyhalogenated contaminants, pharmaceuticals, phytochemicals or veterinary residues. Moreover, this study has for the first time demonstrated the usefulness of the polymeric Oasis HLB and Strata-X sorbents in laboratory and field studies for various microalgal toxins., (Copyright © 2014 Elsevier Ltd. All rights reserved.)

Following a review of official control data on shellfish in France, Ingril Lagoon had been identified as a site where positive mouse bioassays for lipophilic toxins had been repeatedly observed. These unexplained mouse bioassays, also called atypical toxicity, coincided with an absence of regulated toxins and rapid death times in mice observed in the assay. The present study describes pinnatoxin G as the main compound responsible for the toxicity observed using the mouse bioassay for lipophilic toxins. Using a well-characterised standard for pinnatoxin G, LC-MS/MS analysis of mussel samples collected from 2009 to 2012 revealed regular occurrences of pinnatoxin G at levels sufficient to account for the toxicity in the mouse bioassays. Baseline levels of pinnatoxin G from May to October usually exceeded 40 μg kg(-1) in whole flesh, with a maximum in September 2010 of around 1200 μg kg(-1). These concentrations were much greater than those at the other 10 sites selected for vigilance testing, where concentrations did not exceed 10 μg kg(-1) in a 3-month survey from April to July 2010, and where rapid mouse deaths were not typically observed. Mussels were always more contaminated than clams, confirming that mussel is a good sentinel species for pinnatoxins. Profiles in mussels and clams were similar, with the concentration of pinnatoxin A less than 2% that of pinnatoxin G, and pteriatoxins were only present in non-quantifiable traces. Esters of pinnatoxin G could not be detected by analysis of extracts before and after alkaline hydrolysis. Analysis with a receptor-binding assay showed that natural pinnatoxin G was similarly active on the nicotinic acetylcholine receptor as chemically synthesized pinnatoxin G. Culture of Vulcanodinium rugosum, previously isolated from Ingril lagoon, confirmed that this alga is a pinnatoxin G producer (4.7 pg cell(-1)). Absence of this organism from the water column during prolonged periods of shellfish contamination and the dominance of non-motile life stages of V. rugosum both suggest that further studies will be required to fully describe the ecology of this organism and the accumulation of pinnatoxins in shellfish., (Copyright © 2013 Elsevier Ltd. All rights reserved.)

The relationship between azaspiracid shellfish poisoning and a small dinoflagellate, Azadinium spinosum, has been shown recently. The organism produces AZA1 and -2, while AZA3 and other analogues are metabolic products formed in shellfish. We evaluated whether mussels were capable of accumulating dissolved AZA1 and -2, and compared the toxin profiles of these mussels at 24 h with profiles of those exposed to live or lysed A. spinosum. We also assessed the possibility of preparative production of AZA metabolites by exposing mussels to semi-purified AZA1. We exposed mussels to similar concentration of AZAs: dissolved AZA1 + 2 (crude extract) at 7.5 and 0.75 μg L(-1), dissolved AZA1+2 (7.5 μg L(-1)) in combination with Isochrysis affinis galbana, and lysed and live A. spinosum cells at 1 × 10(5) and 1 × 10(4) cell mL(-1) (containing equivalent amounts of AZA1 + 2). Subsequently, we dissected and analysed digestive glands, gills and remaining flesh. Mussels (whole flesh) accumulated AZAs to levels above the regulatory limit, except at the lower levels of dissolved AZAs. The toxin profile of the mussels varied significantly with treatment. The gills contained 42-46% and the digestive glands 23-24% of the total toxin load using dissolved AZAs, compared to 3-12% and 75-90%, respectively, in mussels exposed to live A. spinosum. Exposure of mussels to semi-purified AZA1 produced the metabolites AZA17 (16.5%) and AZA3 (1.7%) after 4 days of exposure, but the conversion efficiency was too low to justify using this procedure for preparative isolation., (Copyright © 2013 Elsevier Ltd. All rights reserved.)

Toxins from the okadaic acid (OA) and azaspiracid (AZA) group cause considerable negative health effects in consumers when present in shellfish above certain levels. The main symptoms, dominated by diarrhoea, are caused by damage to the gastrointestinal (GI) tract. Even though OA and AZAs exert toxicity via different mechanisms, it is important to find out whether they may enhance the health effects if present together since they act on the same organs and are regulated individually. In this study, the main issue was the possibility of enhanced lethality in mice upon combined oral exposure to OA and AZA1. In addition, pathological effects in several organs and effects on absorption from the GI tract were studied. Although the number of mice was small due to low availability of AZA1, the results indicate no additive or synergistic effect on lethality when AZA1 and OA were given together. Similar lack of increased toxicity was observed concerning pathological effects that were restricted to the GI-tract. OA and AZA1 were absorbed from the GI-tract to a very low degree, and when given together, uptake was reduced. Taken together, these results indicate that the present practice of regulating toxins from the OA and AZA group individually does not present an unwanted increased risk for consumers of shellfish., (Copyright © 2012 Elsevier Ltd. All rights reserved.)

Azadinium spinosum (Elbrächter and Tillmann), a small marine dinoflagellate, has been recently described as a de novo producer of azaspiracid-1 and -2 (AZA1 and -2) diarrhoeic toxins. A culture of A. spinosum was established in our laboratory and optimised for pilot-scale production of this organism, to evaluate and understand AZA1 and -2 accumulation and biotransformation in blue mussels (Mytilus edulis) fed with A. spinosum. Adult mussels were continuously exposed to A. spinosum over 1 week in 160 L cylindrical conical tanks. Three different diets were tested for contamination: 5000, 10 000 cells mL(-1) of A. spinosum and a mixture of 5000 cells mL(-1) of A. spinosum with 5000 cells mL(-1) of Isochrysis aff. galbana (T-Iso, CCAP 927/14). During the subsequent period of detoxification (2 weeks), contaminated mussels were continuously fed with 5000 cells mL(-1) of T-Iso. Kinetics of accumulation, detoxification and biotransformation were evaluated, as well as the toxin distribution and the effect of A. spinosum on mussel digestive gland tubules. M. edulis fed on A. spinosum in the three tested conditions; this finding confirmed our recent experiments feeding A. spinosum to mussels. The original algal toxins AZA1 and -2, as well as mussel metabolites AZA3 to 12, -17, -19, -21 and -23 were found during these trials. After as little as 6 h, azaspiracid contents in mussels reached the EU regulatory limit, and metabolites were observed in all conditions at approximately 25% of the total AZA content. This fraction exceeded 50% after 24 h, and continued to increase until the end of the study. AZA17 and -19 were found to be the main metabolites, with AZA17 concentrations estimated in the same order of magnitude as that of the main algal toxin, AZA1., (Copyright © 2012 Elsevier Ltd. All rights reserved.)

For many years, the presence of yessotoxins (YTXs) in shellfish has contributed to the outcome of the traditional mouse bioassay and has on many occasions caused closure of shellfisheries. Since YTXs do not appear to cause diarrhoea in man and exert low oral toxicity in animal experiments, it has been suggested that they should be removed from regulation. Before doing so, it is important to determine whether the oral toxicity of YTXs is enhanced when present together with shellfish toxins known to cause damage to the gastrointestinal tract. Consequently, mice were given high doses of YTX, at 1 or 5 mg/kg body weight, either alone or together with azaspiracid-1 (AZA1) at 200 μg/kg. The latter has been shown to induce damage to the small intestine at this level. The combined exposure caused no clinical effects, and no pathological changes were observed in internal organs. These results correspond well with the very low levels of YTX detected in internal organs by means of LC-MS/MS and ELISA after dosing. Indeed, the very low absorption of YTX when given alone remained largely unchanged when YTX was administered in combination with AZA1. Thus, the oral toxicity of YTX is not enhanced in the presence of sub-lethal levels of AZA1., (Copyright © 2011 Elsevier Ltd. All rights reserved.)

The main aim of this study was to examine absorption and pathological effects of a single sub-lethal dose of the marine biotoxin azaspiracid-1 (AZA1) in mice after oral intubation. When the mice received AZA1 at doses of 100, 200 or 300 μg/kg body weight (b.w.), the toxin was absorbed dose-dependently. Highest concentrations after 24 h were detected in kidneys, spleen and lungs, followed by liver and heart. Only trace amounts were seen in the brain. After seven days, the toxin level had dropped significantly in all organs except for the kidneys. The amount of toxin absorbed was highest in the liver, followed by kidneys, lungs, spleen and heart and the total amount of toxin in the internal organs analysed after 24 h was estimated to be only about 2% of the total amount given for all three dose groups. Pathological changes were only detected in the upper part of the small intestine (duodenum), consisting of mild cellular detachment in the tips of the villi, expansion of the crypts and necrotic changes in lamina propria. In a previous study very long persistence of damage to the gastrointestinal tract by repeated exposures to AZA toxins was reported. In our study, full recovery from the pathological changes was observed seven days after a single exposure to AZA1 at the doses applied., (Copyright © 2010 Elsevier Ltd. All rights reserved.)

During a 10 day survey in the CelticSea near the Irish South-West coast (July 2007), Dinophysis acuta was observed in large numbers. The deployment of a profiler allowed for the identification of a D. acuta thin layer that reached 1910 cells/L. The aim of the study was to investigate if the bloom that occurred in low light environment was viable, dividing, actively producing toxins and if the toxin profile changed over a short term period. Several large concentrates of phytoplankton samples were obtained over a 14 h period, from evening to morning, by pumping Dinophysis from specific depths. In addition, D. acuta was collected in complete darkness at 81 m depth by concentrating 120 L of water. The cells were extracted and their toxin profiles were established by liquid chromatography - mass spectrometry (LC-MS). Passive samplers were deployed in a nearby location for 6 days at 30, 50, 70 and 110 m depth, and the toxin profiles were determined by LC-MS as above. The toxin profiles obtained in phytoplankton samples and in the SPATT were compared and correlated well. Sample concentrates and SPATT results suggested that toxic D. acuta occurred and produced similar toxin profiles at all water depths, including below the euphotic zone., (Copyright © 2010 Elsevier Ltd. All rights reserved.)

Azaspiracids (AZAs) are a group of lipophilic polyether toxins that were discovered in shellfish from Ireland in 1995, following a food poisoning incident. Both the limited availability of pure AZAs and the co-occurrence in shellfish of other toxins in combination with AZAs have so far prevented an in-depth evaluation of the performance of the EU reference test, the mouse bioassay (MBA), for this toxin group at the regulatory limit. The present study evaluated the performance of the mouse bioassay at the example of a mussel tissue homogenate, naturally contaminated with AZAs, diluted with uncontaminated tissues to appropriate concentration levels. Concentrations were determined using liquid chromatography coupled to tandem mass spectrometry (LC-MS-MS) (7 levels ranging from levels less than the limit of quantification to a maximum of ca. 2.24mg/kg in hepatopancreas, which corresponds to a maximum whole flesh AZA1-equivalent of ca. 0.34mg/kg). Replicate homogenates of each concentration level were analysed by MBA on 7 independent occasions over 6 weeks. Inhomogeneity between replicate aliquot portions was evaluated using LC-MS-MS and ranged from 1.8 to 6.6% RSD for the six levels contaminated above quantification limits. This variation was similar to the variability of the LC-MS-MS method within a batch, and the difference between replicate aliquots could thus be considered negligible. Other uncertainties considered in the study included the short- and long-term variability of the LC-MS-MS method, toxic equivalence factors, relative response factors in mass spectrometric detection, additional analogues and matrix effects. A concentration-response curve was modelled as a 4-parametric logistic fit to a sigmoidal function, with an LC(50) of 0.70mg AZA1-equivalent/kg hepatopancreas tissue. Furthermore, the mathematical model of the lethality data from this study suggests that occasional negative mouse assays at high concentrations, previously observed in the Irish statutory monitoring, are at least partly due to the biological variation of mice and can be understood on a statistical basis. The mathematical model of the concentration-response curve also describes the probability of a positive mouse bioassay at the current regulatory limit of 0.16mg/kg to be ca. 95%. Therefore, it appears that the mouse bioassay performs very well in the implementation of this limit. Hence, the present study very strongly suggests that the MBA and LC-MS-MS techniques can be considered equivalent in the implementation of the current regulatory limit of 0.16mg/kg for Azaspiracids in shellfish.

The search for azaspiracids (AZAs) in shellfish on the Portuguese coast started in 2002, but the presence of these toxins could not be demonstrated until the summer of 2006. Analysis by liquid-chromatography-tandem mass spectrometry (LC-MS/MS) allowed the confirmation of AZA2 as a dominant compound, followed by AZA1, in blue mussel (Mytilus galloprovincialis), common cockle (Cerastoderma edule), clams (Venerupis senegalensis, Ruditapes decussatus), razor clam (Solen marginatus) and oyster (Crassostrea spp). Traces of AZA3 were found only in blue mussel. Total levels of AZA1-3 determined in the whole flesh by LC-MS/MS ranged from 1.6 to 6.1 microg/kg. The finding of low levels of AZAs since 2002 suggests a low risk level when compared with the highest risks posed by diarrhetic shellfish poisoning (DSP) and paralytic shellfish poisoning (PSP) toxins. However, the limited number of years studied might generate a misleading conclusion. The contamination with PSP is an example, as no contamination occurred for an extended period of time between 1996 and 2004, despite high levels having occurred outside this period. Thus, there appears overall a moderate likelihood of occurrence of AZAs in the range that may be relevant to consumers.

Using high-performance liquid chromatography with mass spectrometry, the influence of conventional steaming and another heat treatment on the level of okadaic acid and dinophysistoxin-2 in mussels (Mytilus edulis) was investigated. Concentration increases correlated with water loss during steaming, and increased distribution of okadaic acid and dinophysistoxin-2 from the digestive glands to the remainder tissues was observed as a result of the processes examined. This suggests that the analysis of whole flesh tissues, as opposed to dissected digestive glands, is more appropriate for regulatory purposes, particularly if cooked samples are being analysed. A systematic heat treatment experiment showed that while okadaic acid group toxins are stable during cooking processes, degradation does occur in mussel tissues after prolonged exposure to high temperatures. The findings of the studies reported here have importance in terms of the methodology applied in regulatory phycotoxin monitoring programmes. Therefore, options for sample pretreatment are discussed.

When substituting the mouse bioassay for lipophilic marine algal toxins in shellfish with analytical methods, science based factors of relative toxicity for all analogues that contribute to health risk to consumers are necessary. The aim of this paper is to establish the relative intraperitoneal toxicity of dinophysistoxin-2 (DTX-2) compared with okadaic acid (OA). The study was performed as an open, randomised parallel group trial with a four level response surface design within each of the two parallels. In accordance with the response surface design model, the LD50 for DTX-2 and OA was 338 and 206 microg/kg, respectively. By use of common regression analysis, the LD50 of DTX-2 and OA were estimated to 352 microg/kg and 204 microg/kg, respectively. The deviations between the LD50 estimates by the two methods was 4% for DTX-2 and less than 1% for OA. Taken together, these results indicate that the relative toxicity of DTX-2 is about 0.6, compared to OA. Results from the PP2A assay correspond very well with the results obtained by the mouse bioassay. The IC50 concentrations for DTX-2 and OA were 5.94 and 2.81 ng/mL, respectively. This indicates that OA is about twice as toxic as DTX-2. Since inhibition of PP2A is acknowledged as the main mechanism of toxicity of the OA group toxins, this supports the establishment of a relative toxicity factor of DTX-2 of 0.6 compared with OA.

Azaspiracid-1 (AZA-1) is a recently identified phycotoxin that accumulates in molluscs and can cause severe human intoxications. For this study, we utilized murine spinal cord and frontal cortex neuronal networks grown over 64 channel microelectrode arrays (MEAs) to gain insights into the mechanism of action of AZA-1 on neuronal cells. Extracellular recordings of spontaneous action potentials were performed by monitoring mean spike rate as an assay of the efficacy of AZA-1 to alter the bioelectrical activity of neurons in the networks. Via slow onset, AZA-1 decreased the mean spike rate of the spinal cord neurons with an IC(50) of ca. 2.1nM, followed by partial recovery of original activity when toxin was removed. Pre-treatment with the GABA(A) receptor antagonist bicuculline led to an increased response of the neuronal networks to AZA-1 exposure and resulted in an irreversible inhibition of spike rate. AZA-1 did not cause any changes in frontal cortex networks upon drug exposure. In addition, whole-cell patch clamp recordings from spinal cord neurons showed that AZA-1 had no significant effect on the voltage-gated sodium (Na(+)) or calcium (Ca(2+)) currents, suggesting that the toxin affected synaptic transmission in the neuronal networks through a mechanism independent of these voltage-gated channels.

The effect of heat treatment on domoic acid (DA) content in soft tissues of mussels Mytilus edulis was investigated using high performance liquid chromatography. DA concentrations in whole flesh, hepatopancreas and tissue remainder were measured in fresh, steamed and autoclaved mussel flesh. Relative decreases in DA and tissue fluid following heat treatments of whole flesh were similar resulting in approximately equal concentrations of DA pre- and post-treatment. DA concentration decreased in the hepatopancreas and increased in tissue remainder suggesting some organ disruption of mussels during heat treatment. These findings suggest that heat treatments using either conventional steaming or autoclaving at 121 degrees C are not appropriate techniques to reduce DA in mussels during commercial processing. We also conclude that sample pre-treatment has a minimal effect on the result of a DA analysis on whole mussel tissues. The stability of DA at different temperatures within a shellfish matrix was separately tested. Reductions in DA concentration (ca. 3-7%) compensate for some of the discrepancies between what was found in the cooking fluids in the initial study and what was expected based on the whole flesh concentration of the uncooked material.

This study used liquid chromatography coupled to mass spectrometry to identify some parameters important in the analysis of azaspiracids. The first aspect was the distribution of azaspiracids within mussels, in particular the content in the digestive gland as compared to the remaining tissues. In our study, azaspiracids accumulated in the digestive gland, similar to other lipophilic toxins. The ratio of toxin in the digestive gland compared to the whole mussel was on average circa 5, both for a bulk sample collected in Norway in 2004 and for 28 samples from Ireland collected over 3 years (2001-2003). These results may justify the practise to only analyse the digestive gland, a step considered necessary to achieve adequate detection limits for azaspiracids both in the mouse bioassay and other analytical techniques. Steaming of mussels as a sample pre-treatment was found to be another parameter affecting the result. Azaspiracids concentrated indirectly, i.e. through the loss of water or juice from the matrix. The cooked shellfish tissues had a concentration of azaspiracids 2-fold higher than the uncooked shellfish, both for whole flesh and for digestive gland tissue. This finding is of particular importance since it may affect the maximum guidance level at which shellfish may be allowed for human consumption. Finally, parameters affecting the extraction efficiency were studied, including the nature of the extraction solvent, the sample-to-solvent ratio and replicate extraction. The largest differences were observed between different solvents and between different sample-to-solvent ratios, while the effect of replicate extraction was minimal if large sample-to-solvent ratios were used. Duplicate extraction using 100% methanol was found to be the best combination of parameters.

Azaspiracid-1 (AZA-1) is a newly identified phycotoxin reported to accumulate in molluscs from several northern European countries and documented to have caused severe human intoxications. The mechanism of action of AZA-1 is unknown. Our initial investigations have shown that AZA-1 is cytotoxic to a range of cell types. Cytotoxicity was evident in all seven cell types tested, suggesting a broad-spectrum mode of action, and was both time- and concentration-dependent. However, AZA-1 took an unusually long time (>24 h) to cause complete cytotoxicity in most cell types, with the exception of the rat pituitary GH(4)C(1). Extended exposure times did not always lower the EC(50) value for a given cell line, but always resulted in more complete cytotoxicity over a very narrow concentration range. The Jurkat cell line (human lymphocyte T) appeared to be very sensitive to AZA-1, although the EC(50) values (24-72 h) for all the cell types were in the low nanomolar range (0.9-16.8 nM). The effect of AZA-1 on membrane integrity was tested on Jurkat cells and these data confirm our visual observations of cytotoxicity and necrotic cell lysis following exposure of Jurkat cells to AZA-1 and suggest that AZA-1 has some properties unique among marine algal toxins. Additionally, there were dramatic effects of AZA-1 on the arrangement of F-actin with the concurrent loss of pseudopodia, cytoplasmic extensions that function in mobility and chemotaxis. Although these phycotoxin-specific effects of AZA-1 suggest a possible site of action, further work using cell-based approaches is needed to determine the precise mode of action of AZA-1.

Azaspiracid-1 (AZA-1) is a newly identified phycotoxin that accumulates in commercially important bivalve molluscs harvested in several European countries and causes severe human intoxications. Molluscan shellfish are known vectors for accumulation and subsequent transfer of phycotoxins such as brevetoxin and domoic acid through various trophic levels within food webs. Finfish can also accumulate phycotoxins, both directly from toxic algae or from consumption of contaminated shellfish and smaller intoxicated fish. To evaluate the teratogenic potential of AZA-1 and its relevancy to toxin accumulation in finfish, we have utilized a microinjection technique to mimic the maternal-egg toxin transfer of an AZA-1 reference standard and a shellfish extract containing azaspiracids in an embryonic Japanese medaka (Oryzias latipes) fish model. Microinjection of purified AZA-1 caused dose-dependent effects on heart rate, developmental rate, hatching success, and viability in medaka embryos. Within 4 days of exposure to doses > or = 40 pg AZA-1/egg, substantial retardation in development was observed as reduced somatic growth and yolk absorption, and delayed onset of blood circulation and pigmentation. Embryos treated to > or =40 pg AZA-1/egg had slower heart rates (bradycardia) for the 9 days in ovo period, followed by reduced hatching success. Microinjection of a contaminated mussel (Mytilus edulis) extract containing AZAs (AZA-1, -2, and -3), okadaic acid, and dinophysistoxin-2 resulted in similar responses from the fish embryos at equivalent doses. These studies demonstrate that AZA-1 is a potent teratogen to finfish. This work will complement future investigations on AZA-1 accumulation in marine food webs and provide a basis for understanding its toxicity at different trophic levels.