The preparation of certified calibration solutions for azaspiracid-1, -2, and -3, potent marine biotoxins found in shellfish.

The production and certification of a series of azaspiracid (AZA) calibration solution reference materials is described. Azaspiracids were isolated from contaminated mussels, purified by preparative liquid chromatography and dried under vacuum to the anhydrous form. The purity was assessed by liquid chromatography-mass spectrometry and nuclear magnetic resonance spectroscopy. The final concentration of each AZA in a CD(3)OH stock solution was determined by quantitative NMR spectroscopy. This solution was then diluted very accurately in degassed, high purity methanol to a concentration of 1.47 ± 0.08 µmol/L for CRM-AZA1, 1.52 ± 0.05 µmol/L for CRM-AZA2, and 1.37 ± 0.13 µmol/L for CRM-AZA3. Aliquots were dispensed into argon-filled glass ampoules, which were immediately flame-sealed. The calibration solutions are suitable for method development, method validation, calibration of liquid chromatography or mass spectrometry instrumentation and quality control of shellfish monitoring programs.

Evaluation of various pH and temperature conditions on the stability of azaspiracids and their importance in preparative isolation and toxicological studies.

Azaspiracids (AZAs) are a group of shellfish toxins that were discovered in mussels from Irish waters in 1995. Because of the rare occurrence of poisoning incidents, the toxicity of the compounds is a continued matter of debate. Neither their mechanism of action nor their pharmacokinetic behavior has been elucidated, principally because of the lack of standards and reference tissues. Procedures to isolate AZAs from contaminated shellfish or to synthesize them have been developed; in particular, the procedures used for the preparative isolation of these toxins are currently being improved. The present paper describes the stability of AZAs in an array of pH and temperature conditions in methanolic solution, in shellfish tissue, and in aqueous mixtures of acids and shellfish tissues. Strong acids such as hydrochloric and formic acid led to rapid degradation of AZA1 at mM concentration, while the weaker acetic acid required harsher temperature conditions (70 degrees C) and greater concentrations to show similar effects. AZAs showed much greater stability in aqueous acidic mixtures with shellfish tissues, suggesting a significant protective effect of the matrix. A mechanism for the acid-catalyzed degradation is proposed, supported by mass spectral evidence from some of the degradation products. Strong bases (sodium hydroxide) also showed a detrimental effect on AZA1; however, weaker bases (ammonium hydroxide) did not lead to degradation over 24 h at room temperature. Finally, the toxic potential of acid degradation products of AZAs was found to be dramatically reduced compared to the parent compounds, as assessed through cytotoxicity.

Azaspiracid shellfish poisoning: a review on the chemistry, ecology, and toxicology with an emphasis on human health impacts.

Azaspiracids (AZA) are polyether marine toxins that accumulate in various shellfish species and have been associated with severe gastrointestinal human intoxications since 1995. This toxin class has since been reported from several countries, including Morocco and much of western Europe. A regulatory limit of 160 microg AZA/kg whole shellfish flesh was established by the EU in order to protect human health; however, in some cases, AZA concentrations far exceed the action level. Herein we discuss recent advances on the chemistry of various AZA analogs, review the ecology of AZAs, including the putative progenitor algal species, collectively interpret the in vitro and in vivo data on the toxicology of AZAs relating to human health issues, and outline the European legislature associated with AZAs.

Azaspiracid-1 alters the E-cadherin pool in epithelial cells.

Azaspiracids cause severe damages in the epithelium of several organs. In this study we have investigated the effects of azaspiracid-1 (AZA-1) on two epithelial cell lines. Nanomolar concentrations of AZA-1 reduced MCF-7 cell proliferation and impaired cell-cell adhesion. AZA-1 altered the cellular pool of the adhesion molecule E-cadherin by inducing a dose- and time-dependent accumulation of an E-cadherin fragment (E-cadherin-related antigen [ECRA(100)]), with a concentration inducing the half-maximal effect (EC(50)) of 0.47nM. The immunological characterization of ECRA(100) revealed that it consists of an E-cadherin molecule lacking the intracellular domain, and these data showed that the effect induced by AZA-1 in MCF-7 cells is undistinguishable from that induced by yessotoxin (YTX) in the same experimental system. A comparison of toxin effects in MCF-7 and Caco 2 cells confirmed that the effects induced by AZA-1 and YTX are undistinguishable in these cells. Treatment of fibroblasts with AZA-1 did not affect the cellular pool of N-cadherin showing that the toxin effect is cadherin-specific. A comparison of the effects induced by AZA-1, YTX, and okadaic acid on F-actin and E-cadherin in MCF-7 and Caco 2 cells showed that 1nM AZA-1 did not cause significant changes in F-actin and that accumulation of ECRA(100) did not correlate with decreased levels of F-actin under our experimental conditions. Matching our results with those available in literature, we notice that, when molecular effects induced by AZA-1 and YTX have been studied in the same in vitro systems, experimental data show that they are undistinguishable in terms of sensitive cellular parameters, effective doses, and kinetics of responses in several cell lines. The possibility that azaspiracids and YTXs might share their molecular mechanism(s) of action in defined biological settings should be considered.

Relative toxicity of dinophysistoxin-2 (DTX-2) compared with okadaic acid, based on acute intraperitoneal toxicity in mice.

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.

Identification of fatty acid esters of pectenotoxin-2 seco acid in blue mussels (Mytilus edulis) from Ireland.

Pectenotoxins from marine dinoflagellates of the genus Dinophysis are rapidly hydrolyzed by many shellfish to give pectenotoxin-2 seco acid, which isomerizes to 7-epi-pectenotoxin-2 seco acid. Three series of fatty acid esters of pectenotoxin-2 seco acid (PTX-2 seco acid) and 7-epi-PTX-2 seco acid were detected by LC-MS analysis of extracts from blue mussels (Mytilus edulis) from Ireland. The locations of the fatty acid ester linkages were identified by a combination of LC-MSn in positive- and negative-ion modes, LC-MS analysis of the products from reaction of the esters with sodium periodate, and NMR analysis of purified samples of the two most abundant ester derivatives. The 37-O-acyl esters of PTX-2 seco acid were the most abundant, followed by the corresponding 11-O-acyl esters, accompanied by low levels of the 33-O-acyl esters. The most abundant fatty acid esters in the fractionated sample were, in order, the 16:0, 22:6, 14:0, 16:1, 18:4, and 20:5 fatty acids, although a wide array of other PTX-2 seco acid fatty acid esters were also present at low levels.

Discovery of new analogs of the marine biotoxin azaspiracid in blue mussels (Mytilus edulis) by ultra-performance liquid chromatography/tandem mass spectrometry.

Azaspiracids (AZAs) are a group of lipophilic marine biotoxins that were first discovered in blue mussels harvested in 1995 in Killary Harbour on the west coast of Ireland. At least eight people fell ill after the consumption of contaminated mussels and developed symptoms of nausea, stomach cramps, vomiting and severe diarrhoea. Until now, eleven different analogs of these toxins have been described, with a twelfth one theoretically postulated. This paper describes the detection and identification of twenty new analogs of azaspiracid, including dihydroxy-AZAs and carboxy-AZAs, using state-of-the-art techniques including ultra-performance liquid chromatography (UPLC) and tandem mass spectrometry (MS/MS). Blue mussels (Mytilus edulis) from a toxic event of the northwest coast of Ireland in 2005 were extracted and analysed using LC/MS. The mass spectra obtained from different instruments enabled identification of previously unknown analogs of azaspiracid with additional hydroxyl and carboxyl substituents. Mass fragmentation patterns of the dihydroxy-AZAs indicated the positions of these substituents to be at the C3 and C23 position. The previously theoretically postulated AZA12 was also observed in this study. Product ion spectra showed the presence of a unique fragment ion at m/z 408 for all C23-hydroxylated analogs. This fragmentation competes with the fragmentation leading to m/z 362, a fragment ion that has shown to be present in all AZAs. The novel analogs have not been seen in plankton or water samples and are believed to be metabolites of AZAs formed in mussels. All the new AZA analogs were present at low concentrations in the shellfish and it is probably safe to assume that they do not pose a risk for the shellfish consumer.

Feasibility of gamma irradiation as a stabilisation technique in the preparation of tissue reference materials for a range of shellfish toxins.

The effect of gamma-irradiation on concentrations of hydrophilic and lipophilic phycotoxins has been investigated by use of HPLC-UV and LC-MS. Pure toxins in organic solvents and toxins in mussel (Mytilus edulis) tissues were irradiated at three different doses. In solution all toxin concentrations were reduced to some extent. Most severe decreases were observed for domoic acid and yessotoxin, for which the smallest dose of irradiation led to almost complete destruction. For pectenotoxin-2 the decrease in concentration was less severe but still continuous with increasing dose. Azaspiracid-1 and okadaic acid were the least affected in solution. In shellfish tissue the decrease in toxin concentrations was much reduced compared with the effect in solution. After irradiation at the highest dose reductions in concentrations were between ca. 5 and 20% for the lipophilic toxins and there was no statistical difference between control and irradiated samples for azaspiracids in tissue. Irradiation of shellfish tissues contaminated with domoic acid led to a more continuous decrease in the amount of the toxin with increasing dose. The effect of irradiation on the viability of microbial activity in shellfish tissues was assessed by using total viable counting techniques. Microbial activity depended on the type of shellfish and on the pretreatment of the shellfish tissues (with or without heat treatment). As far as we are aware this is the first investigation of the effectiveness of irradiation as a technique for stabilising tissue reference materials for determination of phycotoxins. Our results suggest that this technique is not effective for materials containing domoic acid. It does, however, merit further investigation as a stabilisation procedure for preparation of shellfish tissue materials for some lipophilic toxins, in particular azaspiracids. Chemical structures of the toxins investigated in the study.

Clarification of the C-35 stereochemistries of dinophysistoxin-1 and dinophysistoxin-2 and its consequences for binding to protein phosphatase.

Okadaic acid analogues are well known as protein phosphatase inhibitors and occur naturally in marine shellfish feeding on dinoflagellates of the genus Dinophysis, leading to diarrhetic shellfish poisoning of shellfish consumers. Knowledge of the correct structures for these toxins is important in understanding their toxicology, biochemistry, and biosynthesis. We have performed extensive NMR analyses on okadaic acid (1), dinophysistoxin-1 (DTX-1), and dinophysistoxin-2 (DTX-2) obtained from natural sources. Consequently, we were able to unambiguously deduce the stereochemistries at C-35 for DTX-1 and DTX-2 based on analysis of NMR coupling constants and NOE interactions. Our results revealed that DTX-2 (3) has a stereochemistry opposite to that of DTX-1 (2) at C-35. Molecular modeling of the docking of 1-3 with protein phosphatase-1 and protein phosphatase 2A (PP2A) suggested that the reduced affinity of DTX-2 for PP2A may be due to the newly defined stereochemistry at the 35-methyl group. The implications of these findings for biosynthesis and toxicology are discussed.