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Okadaic acid, useful tool for studying cellular processes.

One of the most interesting groups of substances of marine origin, from structural and pharmacological points of view are polyether toxins, which generally present a great diversity in size and potent biological activities. The subject of this review is limited to okadaic acid (OA). It was the first example of a group of polyether toxins produced by marine microalgae, which is responsible for the natural phenomena known as Diarrhetic Shellfish Poisoning, DSP red tides. These toxins are accumulated in the digestive glands of the shellfish with a disastrous effect upon the shellfish industry in many parts of the world. Thus, it has been demonstrated that OA is a highly selective inhibitor of protein phosphatases type 1 (PP1) and 2A (PP2A), subsequently that it causes dramatic increases in phosphorylation of numerous proteins as well as being a potent tumour promoter. For that reason, OA is an extremely useful tool for studying the cellular processes that are regulated by reversible phosphorylation of proteins as signal transduction, cell division and memory.

Amino Acid Sequence↗

Polyclonal and monoclonal antibodies to PbTx-2-type brevetoxins using minute amount of hapten-protein conjugates obtained in a reversed micellar medium.

Minute amount of Brevetoxin PbTx-3 (400 microg; 0.446 micromol) was converted into an hemisuccinate derivative (PbTx-3 HS) then covalently linked to bovine serum albumin (BSA) and ovalbumin (OVA) in a reversed micellar medium. According to the efficient cyclic synthetic procedure described, the epitope density of the conjugates was around 10 and 20 for OVA and BSA carriers, respectively. The kinetics of antibody production in sequential sera harvested from a single BALB/c mouse immunised by multiple intraperitoneal (i.p.) injections of PbTx-3-BSA conjugate was performed by enzyme-linked immunosorbent assay (ELISA). Two monoclonal antibodies (MAbs) against PbTx-3 were selected from fusion of the mouse immune splenocytes with the P3-X63-Ag 8.653 myeloma cells. In competitive inhibition ELISA experiments, both polyclonal antibodies and MAbs exhibited strong cross-reactivity (> or = 100%) to other PbTx-2-type toxins (PbTx-2 and -9) but low or moderate cross-reactivity (6-15%) to a PbTx-1-type toxin (PbTx-1). Moreover, using these two MAbs, a low cross-reactivity with okadaic acid (3%) was noticed but no significant cross-reactivity was observed with two ciguatoxins (CTX-1B and CTX-3C) over the concentration range studied. The apparent dissociation constant (K(D)) for the interaction of these MAbs with free PbTx-2-type toxins was in the 10(-6)-10(-7)M range. The performance of this MAb-based assay (limit of detection approximately 5ng/well; working range=8-150ng/well) coupled with adequate extraction methods would provide an alternative assay to the mouse i.p. bioassay for routine shellfish monitoring. This production and characterisation of MAbs using small amount of polyether toxins in a reversed micellar medium appear most valuable for the development of immunoassays to other highly potent but poorly available marine polyether toxins like ciguatoxins (CTXs).

Animals↗

Rapid facile solid-phase immunobead assay for screening ciguatoxic fish in the market place.

The precision of the solid-phase immunobead assay (Ciguatect) to detect toxins associated with ciguatera poisoning have been evaluated through analysis of toxic and non-toxic fish obtained from fishing areas around the Hawaiian Islands. The Ciguatect test kit has been optimized for application to field/marketplace screening of ciguatoxic fish. Twelve parrot, surgeon, and amberjack fish fillet and fish extract test portions containing various concentrations of toxins were distributed to participating laboratories for analysis. The presence or absence of ciguatera-related toxins is determined by binding the toxins to a membrane attached to a plastic strip and exposing the toxin ladened membrane to a monoclonal antibody-colored latex bead complex which has a high specificity for ciguatera-related toxins. The intensity of the color on the membrane denotes the presence of the toxins in the fish or fish extract. Toxic components in the fish were confirmed by extraction, column purification, and toxicity testing using the brine shrimp (Artemia sp.) assay. Okadaic acid was used to standardize both the S-PIA and brine shrimp assays. For determination of ciguatoxin and related polyether toxins in parrot, surgeon, and amberjack fish fillets, the relative standard deviations for repeatability (RSDR) were 13.5, 9.0 and 4.3%, respectively, and the relative standard deviations for reproducibility (RSDR) were 44.4, 29.7 and 14.3%, respectively, for concentrations ranging from 1-4 ng/test strip. For determination of ciguatoxin and related polyether toxins in parrot, surgeon, and amberjack fish extracts, the RSDR were 5.8, 4.8, and 3.7%, respectively, and the RSDR were 11.9, 9.9, and 7.6%, respectively, for concentrations ranging from 3-5 ng/test strip.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

The effect of brevenal on brevetoxin-induced DNA damage in human lymphocytes.

Brevenal is a nontoxic short-chain trans-syn polyether that competes with brevetoxin (PbTx) for the active site on voltage-sensitive sodium channels. The PbTxs are highly potent polyether toxins produced during blooms of several species of marine dinoflagellates, most notably Karenia brevis. Blooms of K. brevis have been associated with massive fish kills, marine mammal poisoning, and are potentially responsible for adverse human health effects such as respiratory irritation and airway constriction in beach-goers. Additionally, the consumption of shellfish contaminated with PbTxs results in neurotoxic shellfish poisoning (NSP). The purpose of the present study was to determine whether PbTx could induce DNA damage in a human cell type, the lymphocyte, and if so, whether the damage could be antagonized or ameliorated by brevenal, a brevetoxin antagonist. The DNA damage may occur through both endogenous and exogenous physiological and pathophysiological processes. Unrepaired or erroneously repaired DNA damage may result in gene mutation, chromosome aberration, and modulation of gene regulation, which have been associated with immunotoxicity and carcinogenesis. A single-cell gel electrophoresis assay, or comet assay, was used to determine and compare DNA damage following various treatments. The data were expressed as tail moments, which is the percentage of DNA in the tail multiplied by the length between the center of the head and center of the tail (in arbitrary units). The negative control tail moment was 29.2 (SE=+/-0.9), whereas the positive control (hydrogen peroxide) was 72.1 (1.5) and solvent (ethanol) was 24.2 (2.1). The PbTx-2 (from Sigma, St. Louis, MO, USA), 10(-8) M was 41.3 (3.6), PbTx-9 (Sigma), 10(-8) M was 57.0 (5.3), PbTx-2 (from University of North Carolina at Wilmington, UNCW), 10(-8) M was 49.4 (9.9), and PbTx-3 (UNCW), 10(-8) M was 64.0 (6.4). 1.0 microg/ml brevenal applied 1 h before the PbTxs protected the lymphocytes from DNA damage; PbTx-2 (Sigma), 31.3 (2.1); PbTx-9 (Sigma), 35.5 (2.9); PbTx-2 (UNCW), 33.9 (1.4); PbTx-3 (UNCW), 34.9 (1.25). The tail moment for 1.0 mug/ml brevenal alone was 30.8 (2.6). The results indicate that extensive genotoxic damage is induced by PbTx-2 and 9 (Sigma), and PbTx-2 and 3 (UNCW) in normal human lymphocytes, which is fully antagonized by brevenal. This suggests that the immune systems of individuals exposed to PbTx during harmful algal bloom (HAB) events may be at risk.

Animals↗

Rapid determination of polyether marine toxins using liquid chromatography-multiple tandem mass spectrometry.

The diarrhetic shellfish poisoning (DSP) toxins, okadaic acid (OA), dinophysistoxins (DTX); pectenotoxin-2 (PTX2) and pectenotoxin-2 seco acids, were determined in marine phytoplankton, Dinophysis acuta, and mussels (Mytilus edulis) collected along the southwest coast of Ireland. Liquid chromatography-multiple tandem mass spectrometry (LC-MS/MS) was employed for the simultaneous determination of a series of marine toxins with large polarity differences. Separation of five DSP toxins was achieved on a C18 column (Luna-2, 150 mm x 2.1 mm, 5 microm) using an acetonitrile-water gradient with ammonium acetate as an eluent modifier. Electrospray ionisation (ESI) in negative mode, was used to generate the molecule related ion, [M-H]-, for each toxin. To develop a multiple reaction monitoring (MRM) method, fragmentation studies were performed to determine the optimum precursor-product ion combinations: OA (803/255), DTX2 (803/255), DTX1 (817/255), PTX2SAs (875/137) and PTX2 (857/137). This highly sensitive method had detection limits better than 1 pg (on-column). Linear calibrations were obtained for shellfish extracts that were spiked with toxins, OA, 0.007-1.00 microg/ml (r2 = 0.9993, N = 3) and DTX2, 0.054-8.5 microg/ml (r2 = 0.9992, N = 3). Good reproducibility data were also achieved with %RSD values (N = 3) ranging from 3.15% (0.56 microg DTX2/ml) to 5.71% (0.14 microg DTX2/ml), for shellfish extracts. The method was sufficiently sensitive to permit the determination of DSP toxins in small numbers of picked phytoplankton cells (N = 12-40). In one sample of D. acuta the average toxin composition per cell was: OA (7.0 pg), DTX2 (11 pg) and PTX2 (7.2 pg).

Chromatography, High Pressure Liquid↗

Effect of maitotoxin on guanine nucleotide interaction with G-protein alpha subunits.

Maitotoxin is a potent water-soluble polyether toxin produced by the marine dinofiagellate Gambierdiscus toxicus. Although associated with increased calcium uptake, mobilization of internal calcium stores, and enhanced phosphoinositide metabolism, the primary molecular mechanism underlying its actions remains unclear. In this study, we evaluated the effects of maitotoxin (MTX) on the interaction of guanine nucleotides with G-protein alpha subunits. Equilibrium binding of the nonhydrolyzable GTP analog, GTPgammaS, to alpha subunits (Go, Gs, Gi1, Gi2, and Gi3) was decreased in the presence of MTX. Furthermore, reconstitution of Galpha with Gbetagamma dimer showed a reversal of the inhibition elicited by MTX. GDP/GTP exchange rate for Galpha subunits was significantly inhibited in the presence of MTX. MTX had no effect on the rate of GDP or GTP dissociation from alpha subunits. Also, the mastoparan-induced component of nucleotide exchange is not effected by MTX. These results suggest that MTX acts on Galpha subunits to modulate their interaction with guanine nucleotides, perhaps by stabilizing an empty state of the alpha subunit. Accordingly, MTX may disrupt the normal signal transduction pathways by inhibiting GTP binding to Galpha subunits and interfering with the GDP/GTP exchange.

Animals↗

Behavioral thermoregulatory response to maitotoxin in mice.

Many types of marine algal toxins induce marked hypothermic responses in mice. However, it is not known if the thermoregulatory response to these toxins results from dysfunction in the control of core temperature (Tc) or is a coordinated response to lower Tc as occurs with a variety of xenobiotic insults. Female CD-1 mice were administered purified maitotoxin (338 ng/kg; IP) and placed in a temperature gradient for 5 h that permitted the selection of ambient temperatures (Ta) ranging between 15 and 37 degrees C. Tc was monitored simultaneously by radiotelemetric probes that were surgically implanted into the abdominal cavity at least one week before maitotoxin injection. Maitotoxin led to a rapid reduction in Tc from 37 to 34 degrees C within 30 min after injection. There was a simultaneous 4 degrees C reduction in Ta selected by mice within 15 min after injection. Selected Ta recovered rapidly, increased above baseline for approximately one hour, then remained near baseline levels for the remainder of the test period in the gradient. Tc remained approximately 1 to 2 degrees C below control levels throughout the test period. In the temperature gradient, mice can select Ta's warm enough to offset the hypothermic effects of maitotoxin. That cooler Ta's are selected initially after maitotoxin injection suggest that the central neural control of body temperature is affected by the toxin. We postulate that the hypothermic response may represent an adaptive response to enhance survival following exposure to polyether toxins.

Adaptation, Physiological↗

Liquid chromatography--multiple tandem mass spectrometry for the determination of ten azaspiracids, including hydroxyl analogues in shellfish.

Azaspiracids (AZAs) are a group of polyether toxins that cause food poisoning in humans. These toxins, produced by marine dinoflagellates, accumulate in filter-feeding shellfish, especially mussels. Sensitive liquid chromatography-electrospray ionisation mass spectrometry (LC-ESI-MS(n)) methods have been developed for the determination of the major AZAs and their hydroxyl analogues. These methods, utilising both chromatographic and mass resolution, were applied for the determination of 10 AZAs in mussels (Mytilus edulis). An optimised isocratic reversed phase method (3 microm Luna-2 C18 column) separated 10 azaspiracids using acetonitrile/water (46:54, v/v) containing 0.05% trifluoroacetic acid (TFA) and 0.004% ammonium acetate in 55 min. Analyte determination using MS3 involved trapping and fragmentation of the [M + H]+ and [M + H - H2O]+ ions with detection of the [M + H - 2H2O]+ ion for each AZA. Linear calibrations were obtained for AZA1, using spiked shellfish extracts, in the range 0.05-1.00 microg/ml (r2 = 0.997) with a detection limit of 5 pg (signal : noise = 3). The major fragmentation pathways in hydroxylated azaspiracids were elucidated using hydrogen/deuterium (H/D) exchange experiments. An LC-MS3 method was developed using unique parent ions and product ions, [M + H - H2O - CgH10O2R1R3]+, that involved fragmentation of the A-ring. This facilitated the discrimination between 10 azapiracids, AZA1-10. Thus, this rapid LC-MS3 method did not require complete chromatographic resolution and the run-time of 7 min had detection limits better than 20 pg for each toxin.

Animals↗

[Determination of phycotoxins in aquatic medium by capillary electrophoresis].

Marine phycotoxins present a major public health problem due to their ability to contaminate seafoods. Toxic phytoplankton is not limited, however, to the coastal areas in Europe. There are more and more problems in freshwater reservoirs, in lakes, and in ponds from which grazing animals get their water. Okadaic acid (OA), a polyether toxin from the marine dinoflagellate, Prorocentrum lima, and microcystins (MCYSTs), a potent hepatotoxic cyclic heptapeptides produced by many strains of cyanobacteria have been shown to be a powerful tumor promotor. Thus, considerable effort has been undertaken to find sensitive and easy detection techniques for the determination of phycotoxins from various matrices (microalgae, freshwater, mussels, fish, ...). Different biological and chemical methods have been developed to identify these toxins in shellfish and fish. The mouse bioassay method has been widely used for the detection of toxins such as maitotoxin and ciguatoxin, which are not easily identified by chemical procedures. In this report we describe a capillary electrophoretic method that enables us to detect okadaic acid, microcystins (MCYST-YR, MCYST-LR, MCYST-RR) and maitotoxin in picogram range.

Animals↗

Initial evaluation of the effects of aerosolized Florida red tide toxins (brevetoxins) in persons with asthma.

Florida red tides annually occur in the Gulf of Mexico, resulting from blooms of the marine dinoflagellate Karenia brevis. K. brevis produces highly potent natural polyether toxins, known as brevetoxins, that activate voltage-sensitive sodium channels. In experimental animals, brevetoxins cause significant bronchoconstriction. A study of persons who visited the beach recreationally found a significant increase in self-reported respiratory symptoms after exposure to aerosolized Florida red tides. Anecdotal reports indicate that persons with underlying respiratory diseases may be particularly susceptible to adverse health effects from these aerosolized toxins. Fifty-nine persons with physician-diagnosed asthma were evaluated for 1 hr before and after going to the beach on days with and without Florida red tide. Study participants were evaluated with a brief symptom questionnaire, nose and throat swabs, and spirometry approved by the National Institute for Occupational Safety and Health. Environmental monitoring, water and air sampling (i.e., K. brevis, brevetoxins, and particulate size distribution), and personal monitoring (for toxins) were performed. Brevetoxin concentrations were measured by liquid chromatography mass spectrometry, high-performance liquid chromatography, and a newly developed brevetoxin enzyme-linked immunosorbent assay. Participants were significantly more likely to report respiratory symptoms after Florida red tide exposure. Participants demonstrated small but statistically significant decreases in forced expiratory volume in 1 sec, forced expiratory flow between 25 and 75%, and peak expiratory flow after exposure, particularly those regularly using asthma medications. Similar evaluation during nonexposure periods did not significantly differ. This is the first study to show objectively measurable adverse health effects from exposure to aerosolized Florida red tide toxins in persons with asthma. Future studies will examine the possible chronic effects of these toxins among persons with asthma and other chronic respiratory impairment.

Adolescent↗

Heavy metals, lipid peroxidation, and ciguatera toxicity in the liver of the Caribbean barracuda (Sphyraena barracuda).

Human consumption of over 400 species of tropical fish containing polyether toxins (e.g. ciguatoxins, maitotoxins) causes ciguatera fish poisoning. The Caribbean barracuda (Sphyraena barracuda) is one of the most potent ciguatoxic fish. The objective of this study was to determine whether toxicity of 14 barracuda livers was correlated with lipid peroxidation. A significant correlation (p = 0.015, Pearson's correlation) between lipid peroxidation and toxicity of barracuda liver was found. Because iron and copper are well-known catalysts of hydroxyl radical production and lipid peroxidation in biological systems, the correlation between the concentrations of these metals in barracuda liver and lipid peroxidation and toxicity was also investigated. Cadmium was significantly correlated (p = 0.014) with the toxicity of barracuda livers. This study provides the first data concerning the concentration of iron, copper, and cadmium in the liver of the Caribbean barracuda. Of the three metals studied in barracuda liver, iron was the most abundant, followed by copper and cadmium. Lipid peroxidation was highly variable and detected in five (36%) of the liver samples. Lipid peroxidation was not statistically significantly correlated (p > 0.05) with concentrations of iron, copper, and cadmium in barracuda liver. Collectively, these findings provide additional evidence that lipid peroxidation can be a mechanistic component of ciguatera toxicity in the Caribbean barracuda.

Animals↗

Effect of brevetoxin-B on the neuromuscular transmission of the mouse diaphragm.

The effects of brevetoxin-B, a polyether toxin isolated from Gymnodinium breve Davis, on neuromuscular transmission were studied on the mouse hemidiaphragm using general pharmacological and electrophysiological methods. Brevetoxin-B initially induced spontaneous muscle twitching followed by complete paralysis of the indirectly elicited twitch tension of the mouse diaphragm. The directly elicited muscle twitch tension was not affected and the compound action potential of the phrenic nerve could still be recorded when neuromuscular transmission was completely blocked by the toxin. Brevetoxin-B initially increased, but then decreased, the antidromic activity of the phrenic nerve. Brevetoxin-B increased the frequency of miniature endplate potentials (MEPP), while it decreased the muscle membrane potential. Application of tetrodotoxin (TTX) completely abolished the increase in MEPP frequency and the depolarization of the muscle membrane potential. The results suggested that brevetoxin-B may affect the sodium channels in the nerve terminal and muscle membrane.

Action Potentials↗

A pilot study for the detection of acute ciguatera intoxication in human blood.

INTRODUCTION: Ciguatera fish poisoning arises from consumption of any of the 400 species of tropical marine reef fish containing polyether toxins. No laboratory method is available for clinical diagnosis of acute ciguatera poisoning. The objective of this pilot study was to ascertain the potential usefulness of a bioassay to detect ciguatoxins in humans suspected of acute intoxication. We analyzed plasma of healthy volunteers (asymptomatic negative controls), participants with gastrointestinal (GI) illness but without recent fish consumption (symptomatic negative controls), and participants with GI illness who had recently consumedfish. MATERIALS AND METHODS: Blood samples, questionnaires, and consent forms were collected from 11 symptomatic negative controls and 86 patients that visited emergency rooms in southern Puerto Rico over a 1-year period. Patients had consumed fish within 24 hour prior to the symptoms. Plasma samples were analyzed by a neuroblastoma cell bioassay that detects seafood toxins active at the sodium voltage-gated channel in a dose-dependent fashion. Concentrations were expressed in terms of brevetoxin-1 equivalents (ng PbTx-1 equiv/mL). RESULTS: The mean plasma concentration of 14 asymptomatic negative controls was 39.4 ng PbTx-1 equiv/mL (range 2-74). Of 86 potential ciguatoxic patients who reported fish consumption, 43 had values within the range of normal volunteers, and 9 had concentrations in the nondiagnostic range (73.9-100 ng). Thirty-four patients (40%) had concentrations 3 standard deviations above asymptomatic negative controls (>100 ng PbTx-1 equiv/mL). They had a mean concentration of 1,074 +/- 244.5 ng PbTx-1 equiv/mL (range 101-7,056ng). CONCLUSION: Preliminary findings of elevated PbTx-1 equivalents in 40% of the patients with both ciguatera symptomatology and fish consumption in a geographical area where ciguatera is common suggest that the neuroblastoma bioassay may be a potential diagnostic tool for acute ciguatera intoxication.

Acute Disease↗

Structural elucidation of a new cytotoxin isolated from mussels of the Adriatic sea.

A detailed analysis of the toxic composition in the hepatopancreas of mussels from northern Adriatic sea has been performed. Along with some polyether toxins of DSP (diarrhetic shellfish poisoning) type, such as yessotoxin and its analogues, which are responsible for a variety of human seafood poisonings throughout the world, we have now isolated a new type of toxin, the chlorosulfolipid 1, which is completely different in structure from the polyether DSP-toxins isolated so far. The structural determination of the new toxin, including its absolute stereochemistry, has been performed by extensive NMR analysis and molecular mechanics and dynamics calculations.

Animals↗

Aerosolized red-tide toxins (brevetoxins) and asthma.

BACKGROUND: With the increasing incidence of asthma, there is increasing concern over environmental exposures that may trigger asthma exacerbations. Blooms of the marine microalgae, Karenia brevis, cause red tides (or harmful algal blooms) annually throughout the Gulf of Mexico. K brevis produces highly potent natural polyether toxins, called brevetoxins, which are sodium channel blockers, and possibly histamine activators. In experimental animals, brevetoxins cause significant bronchoconstriction. In humans, a significant increase in self-reported respiratory symptoms has been described after recreational and occupational exposures to Florida red-tide aerosols, particularly among individuals with asthma. METHODS: Before and after 1 h spent on beaches with and without an active K brevis red-tide exposure, 97 persons >or= 12 years of age with physician-diagnosed asthma were evaluated by questionnaire and spirometry. Concomitant environmental monitoring, water and air sampling, and personal monitoring for brevetoxins were performed. RESULTS: Participants were significantly more likely to report respiratory symptoms after K brevis red-tide aerosol exposure than before exposure. Participants demonstrated small, but statistically significant, decreases in FEV(1), midexpiratory phase of forced expiratory flow, and peak expiratory flow after exposure, particularly among those participants regularly using asthma medications. No significant differences were detected when there was no Florida red tide (ie, during nonexposure periods). CONCLUSIONS: This study demonstrated objectively measurable adverse changes in lung function from exposure to aerosolized Florida red-tide toxins in asthmatic subjects, particularly among those requiring regular therapy with asthma medications. Future studies will assess these susceptible subpopulations in more depth, as well as the possible long-term effects of these toxins.

Adolescent↗

Brevetoxin-6 (PbTx-6), a nonaromatic marine neurotoxin, is a ligand of the aryl hydrocarbon receptor.

Brevetoxins (PbTx) are a family of marine polyether toxins that exert their toxic action by activating voltage-sensitive sodium channels. Two forms of brevetoxin, PbTx-2 and -3, induce hepatic cytochrome P4501A1, measured as ethoxyresorufin O-deethylase (EROD) activity, in redfish and striped bass. P4501A1 induction is transcriptionally regulated through the binding of a ligand, typically a planar aromatic compound, to the aryl hydrocarbon receptor (AhR) and subsequent complex formation with the dioxin response element (DRE), an upstream regulatory region of the CYP1A1 gene. To determine if PbTx, a nonaromatic compound, induced EROD by this mechanism, two sets of experiments were performed. Initially, saturation binding assays with PbTx-2, -3, and -6 were carried out to determine if PbTx-2, -3, or -6 was an AhR ligand. Results showed that PbTx-6 inhibited specific binding of dioxin to the AhR, whereas PbTx-2 and -3 had no effect. Subsequently, gel retardation assays showed that PbTx-6 caused a concentration-dependent increase in AhR-DRE complex formation. The most abundant and neurotoxic forms of brevetoxin, PbTx-2 and -3, did not appear to be involved in this process. However, PbTx-6, the epoxide which is a likely biotransformation product, is at least one of the forms of PbTx involved in EROD induction.

Animals↗

Quantitation of diarrhetic shellfish poisoning toxins in Chilean mussel using pyrenyldiazomethane as fluorescent labeling reagent.

Diarrhetic shellfish poisoning (DSP) is a gastrointestinal disease caused by lipid soluble polyether toxins produced by dinoflagellates and accumulated in shellfish. Diarrhetic shellfish poisoning is a worldwide threat to public health and the shellfish industry. To date, only four lipid soluble polyethers have been known as diarrhetic shellfish toxins. Among them, Okadaic acid (OA), Dinophysistoxin 1 (DTX-1, 35-methyl OA), Dinophysistoxin 2 (DTX-2, OA isomers) and Dinophysistoxin 3 (DTX-3, 7-O-acyl-35-methyl OA), all of which have free carboxilic groups. To perform quantitative analysis of DSP toxins in shellfish samples is a requirement, because DSP toxins are endemic in the Chilean mollusks of the southern regions, and although human symptoms of DSP appear relatively mild in comparison with the Paralytic Shellfish Poisoning (PSP), the necessity of monitoring the chronic effects of continued uptake of low doses of DSP toxins more closely is imperative, since DSP toxins have been described as potent tumor promoters. This paper shows the synthesis pathway of a chromophore, 1-pyrenyldiazomethane (PDAM), a fluorescent labeling reagent for determination of carboxilic acids, using High Performance Liquid Chromatography with fluorescence on-line detection. This procedure was developed in order to have a quantitative method for DSP toxins analysis that would be useful for health public services and private shellfish industries. The features of this labeling reagent are compared against ADAM and used for quantitative analysis of DSP toxins in Chilean mussels and cultured dinoflagellates samples.

Animals↗

First evidence of Dinophysistoxin-1 ester and carcinogenic polycyclic aromatic hydrocarbons in smoked bivalves collected in the Patagonia fjords.

Diarrhetic shellfish poisoning (DSP) is a gastrointestinal disease caused by fat-soluble polyether toxins produced by dinoflagellates and accumulated in shellfish. Up to the present, only four fat-soluble polyethers have been known as diarrhetic shellfish toxins. Among them,*** Okadaic acid, Dinophysistoxin-1, Dinophysistoxin-2 and Dinophysistoxin-3. Outbreaks associated with DSP have occurred in the Chilean Patagonia fjords since 1970. Native people, who live in small communities close to the southern fjords, smoke fresh shellfish. During this popular smoking procedure, they impregnate the shellfish with polycyclic aromatic hydrocarbons, as incomplete combustion products, which are potent carcinogenic compounds, this product is sold in local markets without phycotoxins analysis or inclusion in any monitoring program. The present paper shows, DSP phycotoxins quantitation, using high performance liquid chromatography with fluorescent and mass spectrometric detection and the measurements of polycyclic aromatic hydrocarbons by gas chromatography with mass detection, in smoked shellfish samples. The presence of Dinophysistoxin-3, the Dinophysistoxin-1 ester (7-O-acyl-derivatives of dinophysistoxin-1), was assessed in all shellfish samples analyzed. The 7-OH in Dinophysistoxin-1 was esterified with palmitic fatty acid. The shellfish meat contains seven polycyclic aromatic hydrocarbons, among them fluoranthene, phenanthrene, anthracene, pyrene and benzo[a]pyrene. The gas chromatography-mass spectrometry analysis showed four of the six most frequent carcinogenic polycyclic aromatic hydrocarbons reported. The content of benzo[a]pyrene in the Razor Clam and Ribbed Mussel were 78.61 and 4.94 ng/g of shellfish dry weight, respectively. In both cases the benzo[a]pyrene amounts were greater than the acceptable tolerance limits of 1 microg/kg of sample. The Razor Clam samples also show amount further above the maximum label regulated by FAO/WHO (10 microg/kg). The presence of both type of compounds in the smoked shellfish samples analyzed, correspond to a dangerous combination, where the polycyclic aromatic hydrocarbons are carcinogenic compounds by themselves and DTX-1, is a potent tumor promoter.

Animals↗