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The filter-feeding bivalves often accumulate marine toxins by feeding on toxic dinoflagellates that produce marine toxins. Azaspiracids (AZAs) are a group of lipophilic polyether toxins which have been detected in a variety of organisms in many countries. In our present study, accumulation kinetics and toxin distributions in the tissues of seven bivalve species and ascidians relevant to Japanese coastal waters were investigated by experimentally feeding a toxic dinoflagellate Azadinium poporum, which produces azaspiracid-2 (AZA2) as the dominant toxin component. All bivalve species and ascidians investigated in this study had the capability to accumulate AZA2 and no metabolites of AZA2 were detected in the bivalves and the ascidians. Japanese short-neck clams, Japanese oysters, Pacific oysters and ascidians accumulated AZA2 with the highest concentrations on the hepatopancreas, whereas the highest concentrations of AZA2 were found on the gills in surf clams and horse clams. Hard clams and cockles accumulated high levels of AZA2 in both the hepatopancreas and the gills. As far as we know, this is the first report describing detailed tissue distribution of AZAs in several bivalve species other than mussels (M. edulis) and scallops (P. maximus). Variation of accumulation rates of AZA2 in Japanese short-neck clams on different cell densities or temperatures were observed., 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 © 2023 Elsevier Ltd. All rights reserved.)

Portimine, a recently identified cyclic imine produced by the dinoflagellate Vulcanodinium rugosum, has been described as a potent apoptotic agent in contrast to most of the cyclic imines that are well-known to be neurological toxins. As apoptosis can be a consequence of a high level of DNA lesions, we investigated the responses of portimine on several endpoints aimed at detecting DNA damage in the hepatic cell line HepaRG. Portimine induced phosphorylation of H2AX, which could possibly be consistent with the previously published induction of apoptosis with this toxin. In addition, detection of apoptosis through the activation of caspase-3, the induction of strand breaks detected by the comet assay as well as chromosome and genome mutations using the micronucleus assay were addressed. Surprisingly, portimine treatment resulted in increases in only γH2AX in differentiated HepaRG cells whereas no effects on the other endpoints were detected. These increases in γH2AX in the absence of genotoxic effects in the other tests could indicate that portimine could possibly induce a DNA replication stress and/or that the compound can be detoxified by the HepaRG cells., (Copyright © 2021 Elsevier Ltd. All rights reserved.)

A study with DNA microarrays was performed to investigate the effects of two diarrhetic and one azaspiracid shellfish poison, okadaic acid (OA), dinophysistoxin-1 (DTX-1) and azaspiracid-1 (AZA-1) respectively, on the whole-genome mRNA expression of undifferentiated intestinal Caco-2 cells. Previously, the most responding genes were used to develop a dedicated array tube test to screen shellfish samples on the presence of these toxins. In the present study the whole genome mRNA expression was analyzed in order to reveal modes of action and obtain hints on potential biomarkers suitable to be used in alternative bioassays. Effects on key genes in the most affected pathways and processes were confirmed by qPCR. OA and DTX-1 induced almost identical effects on mRNA expression, which strongly indicates that OA and DTX-1induce similar toxic effects. Biological interpretation of the microarray data indicates that both compounds induce hypoxia related pathways/processes, the unfolded protein response (UPR) and endoplasmic reticulum (ER) stress. The gene expression profile of AZA-1 is different and shows increased mRNA expression of genes involved in cholesterol synthesis and glycolysis, suggesting a different mode of action for this toxin. Future studies should reveal whether identified pathways provide suitable biomarkers for rapid detection of DSPs in shellfish., (Copyright © 2017 The Authors. Published by Elsevier Ltd.. All rights reserved.)

Azaspiracids (AZAs) are the most recently discovered group of biotoxins and are the cause of azaspiracid shellfish poisoning (AZP) in humans. To date over thirty analogues have been identified. However, toxicological studies of AZAs are limited due to the lack of availability of toxins and toxin standards. Most data available are on acute toxicity and there are no data available on genotoxicity of AZAs. This study presents an integrated approach investigating the genotoxic potential of AZA1-3 in cell culture systems using the Comet assay combined with assays to provide information on possible apoptotic processes, cytotoxicity and changes in cell number. Results demonstrate a time and dose dependent increase in DNA fragmentation in most cell lines, indicating a genotoxic effect of AZA1-3. However, a significant reduction in cell number and a clear shift from early to late apoptosis was observed for all analogues in Jurkat T cells and HepG-2 cells; CaCo-2 cells did not show a clear apoptotic profile. Late apoptotic/necrotic cells correlate well with the percentage of tail DNA for all analogues in all three cell lines. All data taken together indicate that AZA1-3 is not genotoxic per se and demonstrate apoptotic/necrotic processes to be involved to some extent in AZAs toxicity. The sensitivities of cell lines and the different potencies of AZA1-3 are in agreement with the literature available. The order of sensitivity for all three AZAs tested in the present study is, in increasing order, CaCo-2 cells < HepG-2 cells < Jurkat T cells. The order of potency of AZA1-3 varies among the cell lines., (Copyright © 2016 Elsevier Ltd. All rights reserved.)

The aim of this study was to investigate (i) the cytotoxic effects of lipophilic phycotoxins, including okadaic acid (OA) and dinophysistoxin-1 and -2 (DTX-1 and DTX-2), pectenotoxin-2 (PTX-2), yessotoxin (YTX), spirolide (SPX), and azaspiracids-1, -2 and -3 (AZA-1, AZA-2 and AZA-3), in human HepaRG cells using a multiparametric high content analysis approach, (ii) the ability of nine lipophilic phycotoxins to act as PXR agonists in a HepG2-PXR cell line, (iii) their potential to induce CYP450 activity, and (iv) the role of CYP3A4 in cytotoxicity induced by lipophilic phycotoxins. Our results indicate that while OA, DTX-1 and DTX-2 activated PXR-dependent transcriptional activity in HepG2 cells, no increase of CYP450 (1A2, 3A4, 2C9, 2C19) activities were observed in HepaRG cell following a 72h treatment with these toxins. Multiparametric analysis showed that OA, DTX-1, DTX-2, and PTX-2 were highly cytotoxic in HepaRG cells; inducing cell loss, activation of caspase-3 and γ-H2AX formation. However, no toxicity was observed for YTX, SPX, and AZAs. Moreover, we found that inhibition of CYP3A4 activity by ketoconazole enhances the toxic effects of OA, DTX-1, DTX-2, and PTX-2 in HepaRG cells. Taken together, these results suggest that CYP3A4-mediated metabolism of some lipophilic phycotoxins decreases their in vitro toxicity., (Copyright © 2016 Elsevier Ltd. All rights reserved.)

Among toxin-producing dinoflagellates of the genus Alexandrium, Alexandrium ostenfeldii is the only species able to produce paralytic shellfish poisoning (PSP) toxins, spirolides (SPXs) and gymnodimines (GYMs). In this study we characterized and compared three A. ostenfeldii strains isolated from the Baltic, Mediterranean, and southern Chile Seas with respect to their toxin profiles, morphology, and phylogeny. Toxin analyses by HPLC-FD and LC-HRMS revealed differences in the toxin profiles of the three strains. The PSP toxin profiles of the southern Chile and Baltic strains were largely the same and included gonyautoxin (GTX)-3, GTX-2, and saxitoxin (STX), although the total PSP toxin content of the Chilean strain (105.83 ± 72.15 pg cell(-1)) was much higher than that of the Baltic strain (4.04 ± 1.93 pg cell(-1)). However, the Baltic strain was the only strain that expressed detectable amounts of analogues of GYM-A and GYM-B/-C (48.27 ± 26.12 pg GYM-A equivalents cell(-1)). The only toxin expressed by the Mediterranean strain was 13-desmethyl SPX-C (13dMeC; 2.85 ± 4.76 pg cell(-1)). Phylogenetic analysis based on the LSU rRNA showed that the studied strains belonged to distinct molecular clades. The toxin profiles determined in this study provide further evidence of the taxonomic complexity of this species., (Copyright © 2015 Elsevier Ltd. All rights reserved.)

Fluorescent molecules are regularly utilised to study ligand-receptor interactions. Many ligands for nicotinic receptors have been conjugated with fluorophores to study receptor kinetics, recycling and ligand binding characteristics. These include small agonist molecules, as well as large peptidic antagonists. However, no small molecule antagonists have been investigated using this method. Pinnatoxin F is a newly discovered non-peptidic muscle type nicotinic receptor antagonist produced by the marine dinoflagellate species Vulcanodinium rugosum. This molecule has the potential for conjugation to a fluorophore, allowing subsequent visualisation of interactions with nicotinic receptors. Pinnatoxin F was modified by addition of diaminopolyether spacers, to which a fluorophore (VivoTag(®) 645) was conjugated. The fluorescent pinnatoxin was then applied to muscle sections from thy1-YFP-H transgenic mice, which express YFP in motor nerves, to allow direct visualization of fluorescent binding at the neuromuscular junction. The addition of both the diaminopolyether spacer and the VivoTag(®) 645 reduced the potency of pinnatoxin F, as evidenced by a reduction in in vitro neuromuscular blocking activity and in vivo toxicity. Despite this reduced potency, the fluorescent molecule selectively labelled endplate regions in thy1-YFP mouse muscle sections and this labelling was inhibited by pre-exposure of muscle sections to native pinnatoxin F or the nicotinic antagonist α-bungarotoxin. This study proves nicotinic receptor binding activity of pinnatoxin F and is the first example of a fluorophore-conjugated small-molecule antagonist for nicotinic receptors. These results indicate the potential for other small-molecule nicotinic receptor antagonists to be fluorescently labelled and used as probes for specific nicotinic receptor subtypes., (Copyright © 2014 Elsevier Ltd. All rights reserved.)

Pinnatoxins are produced by dinoflagellates and belong to the cyclic imine family of toxins. They are fast-acting and highly toxic when administered in vivo in rodent bioassays, causing death by respiratory depression within minutes. Studies have revealed that some cyclic imine toxins cause their toxicity by antagonizing both muscle type and heteromeric and homomeric neuronal nicotinic acetylcholine receptors (nAChRs). Pinnatoxins E, F and G all display potent toxicity in in vivo bioassays, with symptoms of toxicity similar to other cyclic imine toxins. However, very little work has been done on the mechanism of action of these pinnatoxin isomers. Thus the aim of the current study was to investigate the rank order of potency and mechanism of action of pinnatoxins E, F and G. The effects of pinnatoxin E, F and G on in vitro rat hemidiaphragm preparations were investigated using twitch tension and electrophysiological techniques to determine the effects of these toxins on cholinergic transmission at the neuromuscular junction. Pinnatoxins E, F and G all produced concentration-dependent reductions in the nerve evoked twitch response of the rat hemidiaphragm, with IC50 values ranging from 11 to 53 nM and a rank order of potency of F > G > E. Only complete washout of pinnatoxin E was evident, with pinnatoxins F and G displaying slow and incomplete washout profiles. Pinnatoxins F and G also reduced the amplitudes of spontaneous miniature endplate potentials and evoked endplate potentials at the neuromuscular junction, without affecting miniature endplate potential frequency or the resting membrane potential of the muscle fibres. These results show that pinnatoxins E, F and G are all potent neuromuscular blocking agents and cause toxicity by acting as antagonists at muscle type nicotinic acetylcholine receptors., (Copyright © 2013 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.)

Gymnodimine-A and 13-desmethyl spirolide C are marine toxins belonging to the cyclic imine group produced by Karenia selliformis and Alexandrium ostenfeldii/peruvianum dinoflagellates, respectively. The aim of this work was to analyze the pharmacological properties of both toxins (at sub-lethal doses) on neuromuscular excitability, when injected locally to isoflurane-anesthetized mice, using a multimodal minimally-invasive in vivo electrophysiological approach. The main effect of both toxins was a marked reversible time- and dose-dependent decrease of the compound muscle action potential recorded from the tail muscle in response to caudal motor nerve stimulation. The dose-response curves of gymnodimine-A and 13-desmethyl spirolide C effect on the maximal amplitude of compound muscle action potential revealed 50% inhibitory doses of 51 ng/mouse (i.e. 1.6 μg/kg or 3.3 nmol/kg mouse) and 0.18 ng/mouse (i.e. 6 ng/kg or 0.01 nmol/kg mouse), respectively. The blocking effect occurred without significant modification of motor nerve excitability parameters. It is concluded that the inhibition of the mouse compound muscle action potential, induced by gymnodimine-A and 13-desmethyl spirolide C, results from an action of these toxins at the level of the skeletal neuromuscular junction, since both cyclic imine toxins are known to interact and block muscle-type nicotinic acetylcholine receptors. In the present in vivo study, 13-desmethyl spirolide C was about 300 fold more active than gymnodimine-A on equimolar basis. The present in vivo approach, associated to recent progress in chemical synthesis of cyclic imine toxins, paves the way for more detailed structure-activity studies to obtain new and more potent synthetic analogs., (Copyright © 2013 Elsevier Ltd. All rights reserved.)

The acute toxicities to mice of pinnatoxins E, F and G, members of the cyclic imine group of phycotoxins, by intraperitoneal injection and/or oral administration, have been determined. These substances were all very toxic by intraperitoneal injection, with LD(50) values between 12.7 and 57 μg/kg. Pinnatoxin E was much less toxic by oral administration than by intraperitoneal injection, but this was not the case for pinnatoxin F. The median lethal doses of the latter substance by gavage and by voluntary intake were only 2 and 4 times higher than that by injection. The high oral toxicity of pinnatoxin F raises concerns as to the possibility of adverse effects of this substance in shellfish consumers, although it should be noted that no toxic effects in humans have been recorded with pinnatoxins or with any other compound of the cyclic imine group., (Copyright © 2012 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.)

Fast-acting cyclic imines belonging to the pinnatoxin and pteriatoxin group of toxins were originally identified in shellfish of the genera Pinna and Pteria in Japan, after food poisoning events in China linked to consumption of Pinna spp. Recently, a range of new and known pinnatoxin analogs has been identified in shellfish, sediment, and seawater samples from Australia and New Zealand. Although the structurally closely-related spirolide toxins are better known, and have a worldwide distribution including Norway and other parts of Europe, the presence of pinnatoxins has not been reported in European waters or shellfish. Here we report results from a survey of Norwegian blue mussels for the presence of pinnatoxins and spirolides, by LC-MS/MS analysis of extracts obtained as part of Norway's routine monitoring programme for regulated algal toxins during late autumn and early winter 2009. Spirolides and pinnatoxin G were widespread (pinnatoxin G (1), spirolide C (2), iso-spirolide C (3), 13-desmethylspirolide C (4), 13,19-didesmethylspirolide C (5), and 20-methylspirolide G (6) were detected in 69%, 13%, 60%, 22%, 33%, and 77%, respectively, of the shellfish samples) and, although levels were generally low, concentrations of up to 115 μg/kg of pinnatoxin G (1) and 226 μg/kg of 13-desmethylspirolide C (4) were detected. We also analyzed stored extracts from passive sampling disks deployed as part of a separate study in autumn 2007. All the stored extracts contained 20-methylspirolide G (which predominated at most locations), most contained pinnatoxin G (73%) and 13,19-didesmethylspirolide C (67%), but iso-spirolide C (36%) and 13-desmethylspirolide C (52%) were also detected in many of the samples. These results suggest that pinnatoxins may be much more widespread than previously suspected, and indicate that they or related compounds could be responsible for sporadic incidents of rapid-onset symptoms during mouse bioassays of shellfish in Europe and elsewhere. The toxicological significance of these levels of pinnatoxins and spirolides is at present unclear. However, although pinnatoxins appear to be less toxic than spirolides by intraperitoneal injection in the mouse bioassay, recently published preliminary toxicological data indicate that pinnatoxins may be as much as an order of magnitude more toxic than spirolides by oral ingestion via food., (Copyright © 2011 Elsevier Ltd. All rights reserved.)

Members of the cyclic imine group of toxins, gymnodimine and spirolides, have been found to be potent antagonists of both muscle type and neuronal nicotinic acetylcholine receptors. These toxins exhibit fast acting toxicity in vivo, causing death within minutes by respiratory depression. This toxicity is shared by the novel cyclic imine pinnatoxins E and F, produced by marine dinoflagellates and recently isolated from New Zealand shellfish. However, there is currently very little data available regarding the mechanism of action for any of the pinnatoxins, and no data at all on the novel pinnatoxins E and F. The aim of the current study was to investigate potential antagonism of nicotinic acetylcholine receptors by pinnatoxins E and F using two in vitro tissue preparations. Compound muscle action potentials elicited by stimulation of the phrenic nerve were recorded from the hemidiaphragm in order to test effects on muscle type heteromeric nicotinic receptors, while effects on α7 homomeric neuronal nicotinic receptors were investigated by recording gamma oscillations in response to tetanic stimulation of the CA1 region of the hippocampus. Both a crude extract containing a mixture of pinnatoxins E and F, as well as pure pinnatoxin F, had no effect on gamma oscillation spectral density or spike count at any concentrations. Conversely, at these same concentrations, both crude and pure pinnatoxin caused an almost complete abolition of nerve-evoked hemidiaphragm action potential responses, without any effect on electrically-evoked (direct) responses. This neuromuscular block could not be reversed by neostigmine. These results show that pinnatoxins E and F block neuromuscular transmission and suggest that observed in vivo muscle paralysis by pinnatoxin is due to selective antagonism of muscle type nicotinic acetylcholine receptors., (Copyright © 2011 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.)

Alexandrium ostenfeldii is a widespread toxic dinoflagellate that has recently bloomed across the Adriatic Sea, seriously threatening both shellfish consumers and aquacultures. In 2007 we reported on preliminary studies carried out on field samples and cultures of A. ostenfeldii. At the time, along with three major spirolides - among which 27-hydroxy-13,19-didesmethyl spirolide C (3) proved to be a novel compound - a number of new minor spirolides were detected. Unfortunately, for all of them only Mass Spectrometry-based structural hypotheses could be ventured due to their very small amount. In the present paper we report on isolation and High Resolution Mass Spectrometry- and NMR-based structural elucidation of two of those minor spirolides detected in our previous study., (Copyright © 2010 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.)

This paper reports on the determination of toxin profile of mussels (Mytilus galloprovincialis) collected in November-December 2003 along the Emilia Romagna coasts (Italy) when a high concentration of Alexandrium ostenfeldii cells was detected in seawater. Detailed liquid chromatography-mass spectrometry (LC-MS) analyses were performed on the crude extracts in both selected ion monitoring (SIM) and multiple reaction monitoring (MRM) modes. They revealed that M. galloprovincialis had accumulated the three major spirolides produced by the alga, namely 13-desMethyl spirolide C, 13,19-didesMethyl spirolide C and 27-hydroxy-13,19-didesMethyl spirolide C, which fully accounted for toxicity of lipophilic extracts shown in mouse bioassay. Interestingly, yessotoxin (YTX) and its analogues were still present in mussel polar extracts but YTX itself was not the major toxin contained in mussels. The presence of pectenotoxin-2 seco acid (PTX-2sa) and its putative epimer was also assessed. The presence of azaspiracids, never reported from the Adriatic sea, as well as of diarrhetic shellfish poisoning toxins (okadaic acid, dinophysistoxins and OA esters) and domoic acid, long known as contaminants of Adriatic mussels, was also investigated., (Copyright 2009 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 French Phytoplankton and Phycotoxins monitoring network (REPHY) recently found positive or dubious negative shellfish samples using lipophilic toxins mouse bioassay. These samples were analyzed by liquid chromatography (LC) in combination with mass spectrometry (MS) to detect the following toxins: okadaic acid (OA), dinophysistoxins (DTXs), pectenotoxins (PTXs), azaspiracids (AZAs), yessotoxins (YTXs), spirolides (SPXs) and gymnodimines (GYMs). Over the 2006-2007 period, chemical analyses revealed various lipophilic toxin profiles according to shellfish sampling locations. In addition to OA and/or PTX-2 and their derivatives, several other compounds were found for the first time in France: (1) during the summer of 2006, AZA-1 and AZA-2 in Queen scallops (Aequipecten opercularis) from Northern Brittany; (2) during the summer of 2007, YTX and its major metabolites (45-hydroxy-YTX, homo-YTX, carboxy-YTX) in shellfish from the Mediterranean coast. Regarding YTX-group, the toxin profiles evolution in mussels during summer showed that: (i) the carboxy-YTX depuration rate was much slower than the YTX and 45-hydroxy-YTX ones; (ii) the homo-YTX concentration, which was initially very weak, increased significantly during the last depuration phase, which seems to reveal a YTX-group high metabolisation level in mussels. This paper reports for the first time on AZA and YTX-groups detection in French shellfish.

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.

Toxicological effects of orally administered azaspiracid (AZA), a new toxin isolated from mussels, were investigated. First, a total of 25 mice were administered AZA twice at 300-450 microg/kg doses and observed for recovery processes from severe injuries. Slow recoveries from injuries were revealed: erosion and shortened villi persisted in the stomach and small intestine for more than 3 months: edema, bleeding, and infiltration of cells in the alveolar wall of the lung for 56 days; fatty changes in the liver for 20 days; and necrosis of lymphocytes in the thymus and spleen for 10 days. Secondly, low doses of AZA (50, 20, 5 and 1 microg/kg) were administered twice a week up to 40 times to four groups of mice. Many mice, nine out of ten at 50 microg/kg and three out of ten at 20 microg/kg, became so weak that they were sacrificed before completion of 40 injections. All these mice showed interstitial pneumonia and shortened small intestinal villi. Most importantly, lung tumor were observed in four mice, one out of ten (10%) at 50 microg/kg and three out of ten (30%) at 20 microg/kg. Tumors were not observed in 11 mice treated at lower doses and in 19 control mice. Hyperplasia of epithelial cells was also observed in the stomach of six mice out of ten administered at 20 microg/kg.

There is an urgent need for an alternative to the mouse bioassay for the detection of algal toxins in shellfish on both analytical and animal welfare grounds. Several alternative methodologies have been described, but have not gained widespread acceptance to date, because each assay measures only one or a small number of related phycotoxins out of the increasing range that needs to be detected. A simple cytotoxicity assay using either the HepG2 or ECV-304 cell lines is described with two end-point measurements, which can detect and distinguish between two unrelated classes of phycotoxins. Morphological examination following 3h exposure to the sample enables the detection of the diarrhetic shellfish poisons, including okadaic acid and related toxins. Viability testing using MTT (3-[4,5-dimethylthiazol-2-yl]-2,5-diphenyl tetrazolium bromide), following 24h exposure of the same cells to the sample, reveals a second class of toxin, which is most probably the newly-described toxin, azaspiracid. This assay should play an important role in shellfish monitoring in the future.

A new type of food poisoning resulting from ingestion of mussels produced in Ireland occurred in the Netherlands in 1995 and then reoccurred in Ireland in 1997. As the causative agent, azaspiracid, was isolated in pure form and revealed to have a structure entirely unlike other known algal toxins, in vivo studies with mice were carried out to elucidate the pathological injuries caused by the toxin. By per os administration, the toxin caused necrosis in the lamina propria of the small intestine and in lymphoid tissues such as thymus, spleen and the Peyer's patches. Both T and B lymphocytes were injured. Additionally a fatty change was observed in the liver. These injuries distinctly differed from those caused by the representative diarrhetic shellfish toxin, okadaic acid.