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Purification and characterization of paralytic shellfish toxin transforming enzyme from Mactra chinensis.

A carbamoylase, which catalyzes hydrolysis of the carbamoyl (or N-sulfocarbamoyl) moiety of paralytic shellfish toxins, was purified from the digestive glands of the Japanese clam Mactra chinensis. Using five steps of column chromatography, 290 microg of Carbamoylase I showing homogeneity on SDS-PAGE was obtained. Carbamoylase I was revealed to be a glycoprotein, having estimated molecular weight of 190 kDa. Observation of single band equivalent to 94 kDa on SDS-PAGE under reducing conditions suggested it to be a homodimer. The optimal temperature and pH were 20 degrees C and 7.0. Carbamoylase I did not require a divalent cation and its activity was inhibited by the serine proteinase inhibitors, benzenesulfonyl fluoride and 4-(2-aminoethyl)-benzenesulfonyl fluoride. Carbamoylase I hydrolyzed both carbamate and N-sulfocarbamate toxins. The presence or absence of a hydroxyl moiety at the N-1 position of the substrate toxins did not significantly alter the reaction rate, but the stereochemistry of sulfate esters at C-11 greatly affected it. The K(m) was 3.02 microM for saxitoxin as a substrate. Nineteen amino acids of the N-terminal sequence were identified by the Edman method. MALDI-TOF-MS/MS spectra of (18)O-labeled tryptic peptides indicated the possible internal amino acid sequences of five peptides.

Amino Acid Sequence↗

Accumulation of paralytic shellfish toxins (PST) from the cyanobacterium Aphanizomenon issatschenkoi by the cladoceran Daphnia magna.

In order to access the effects of Paralytic Shellfish Toxins (PST) in freshwater environment, the accumulation of PST produced by the cyanobacteria Aphanizomenon issatschenkoi in juvenile Daphnia magna was investigated. D. magna was exposed to A. issatschenkoi cells (1.2 x 10(6) cells ml(-1)) for 6, 8, 12, 24 and 30 h and also to lyophilised material (1 mg ml(-1)) for 24h. Survival and somatic growth of the juvenile D. magna was investigated, as was the activity of the biotransformation enzyme system glutathione-S-transferases (GSTs). Between 643+/-65.35 and 1170+/-51.72 pmol PST ml(-1) were detected by HPLC-FLD in D. magna culture medium containing cells and 2745+/-64.61 pmol PST toxin ml(-1), in the medium containing lyophilised material. PST were detected in D. magna tissues in cells exposure (between 6.51 x 10(-2)+/-1.37 x 10(-2) and 3.78 x 10(-1)+/-1.15 x 10(-2)pmol PST animal(-1)). In D. magna exposed to lyophilised material the mean (+/-SD) PST concentration was found to be 6.96 x 10(-3) (+/-3.84 x 10(-3)) pmol PST animal(-1). Following exposure to 1.2 x 10(6) cells ml(-1)A. issatschenkoi fresh cells growth and survival of D. magna were reduced. D. magna exposed to the two A. issatschenkoi treatments (fresh cells and lyophilised material), showed a reduction in activity of the cytosolic glutathione-S-transferases (cGSTs). The results of this study indicate that D. magna can accumulate PST toxins and that the cyanobacterium A. issatschenkoi affects both the fitness and growth potential of juvenile D. magna.

Animals↗

Accumulation and depuration rates of paralytic shellfish poisoning toxins in the shore crab Telmessus acutidens by feeding toxic mussels under laboratory controlled conditions.

Accumulation and depuration rates of paralytic shellfish poisoning toxins (PSP) in the crab Telmessus acutidens were investigated by feeding toxic and non-toxic mussels under laboratory controlled conditions. The crab accumulated toxins in the hepatopancreas in proportion to the amount of toxic mussels they ingested, and the toxicity in the crab hepatopancreas became 3.2 fold of that in the prey mussels after 20 days of feeding. During depuration, a fast reduction of the total toxicity was observed in the crab, and the retention rate of the toxicity after 5 days depuration with feeding of non-toxic mussels was 45.8+/-18.7%. The reduction of the toxicity was moderated in the later period of depuration, and the retention rates of the total toxicity after 10 and 20 days were 54.1+/-29.8% and 14.5+/-9.0%, respectively. The toxin profiles in the crab and mussel were investigated by high performance liquid chromatography, and reductive conversions of the toxins were observed when the toxins were transferred from the mussel to the crab. Consequently, high concentrations of GTX2 and GTX3, and STX that were not detected in the prey mussels, were found in the crab.

Animals↗

Paralytic shellfish toxin profiles and toxin variability of the genus Alexandrium (Dinophyceae) isolated from the Southeast China Sea.

Paralytic shellfish toxin (PST) profiles of 16 Alexandrium isolates from the Southeast China Sea were analyzed by high-pressure liquid chromatography. Toxin content and composition of three A. tamarense isolates, ATDH01, ATGX02 and ATMJ02, were also investigated at different growth phases and under various culture conditions. Our results showed that six strains of A. affine were non-toxic, while 10 strains of A. tamarense and A. catenella were toxic. These toxic isolates grown in the same culture conditions consistently produced an unusually high proportion of the N-sulfocarbamoyl toxin C1/2 (around 60-80% of total toxins) and medium amounts of gonyautoxin GTX5 (around 15-30% of total) with only trace quantities (<5% of total) of other saxitoxin derivatives (i.e. GTX1, GTX3, GTX4 and neoSTX). The toxin composition of three A. tamarense isolates did not vary with the growth phases, although higher toxin contents (Qt, fmolcell(-1)) were found in the exponential phase. Variations in temperature, salinity and nutrient levels affected toxin content of three A. tamarense isolates but they did not have pronounced effects on the toxin composition (mole %). These results indicate that toxin composition remained relatively constant under various culture conditions, suggesting that toxin composition could be used as a stable biomarker for the Alexandrium species in this region. However, comparison of toxin profiles between isolates from different localities require special caution since isolates even from the same region can have distinct toxin profiles.

Animals↗

Transfer and metabolism of paralytic shellfish poisoning from scallop (Chlamys nobilis) to spiny lobster (Panulirus stimpsoni).

The transfer and transformation of paralytic shellfish poisoning (PSP) from scallop Chlamys nobilis to spiny lobster Panulirus stimpsoni were investigated in the present study. The results demonstrate that transfer and transformation of PSP toxins occurred when Panulirus stimpsoni were fed with toxic viscera of Chlamys nobilis, but depurated with non-toxic squids. Additionally, only the lobster hepatopancreas were found to contain PSP, and the toxin profiles were the same with those in the viscera of the scallop, including carbamate toxins (GTX(1-3)), N-sulfocarbamoyl toxins (C(1+2) and B(1)) and decarbamoyl toxins (dcGTX(2+3)). Unlike the lobster, the scallop contained more alpha than beta toxins. After being fed with toxic Chlamys nobili for 6 d, Panulirus stimpsoni selectively accumulated N-sulfocarbamoyl toxins with low toxicity. However, when they were depurated with non-toxic squid, N-sulfocarbamoyl toxins tended to transform into carbamate toxins with higher toxicity. The concentration of dcGTX(2+3) in Panulirus stimpsoni decreased significantly and wasn't detectable after depuration for 6 d, which was likely due to their initial low accumulation of toxins. These results reveal that PSP could be transferred and transformed in Crustaceans along the given food chain under the conditions of laboratory, but there are many questions remained to be solved, and the further studies should be carried out.

Animals↗

Liquid chromatography-electrospray ionization mass spectrometry of the diarrhetic shellfish-poisoning toxins okadaic acid, dinophysistoxin-1 and pectenotoxin-6 in bivalves.

Determination of diarrhetic shellfish-poisoning (DSP) toxins, okadaic acid (OA), dinophysistoxin-1 (DTX1) and pectenotoxin-6 (PTX6) was carried out by liquid chromatography (LC) followed by on-line atmospheric pressure electrospray ionization-mass spectrometric (ESI-MS) detection with a heated capillary interface. Mass spectra of authentic OA, DTXI and PTX6 standards exhibited abundant [M-H] at m/z 803, 817 and 887, respectively. Linearity of peak area obtained by selected-ion monitoring (SIM) for [M-H]- of each toxin was confirmed over a wide range of concentrations from 10 pg to 30 ng. LC-ESI-MS analysis of OA, DTX1 and PTX6 in scallops and mussels, collected at the same site (Mutsu Bay, Japan), was carried out. Scallops and mussels collected at the same site showed different toxin profiles. Although PTX6 was detected from scallops, it was not detected from mussels.

Animals↗

Quantitative determination of marine toxins associated with diarrhetic shellfish poisoning by liquid chromatography coupled with mass spectrometry.

Quantitative determination by liquid chromatography (LC) coupled with mass spectrometry (MS) was achieved for the following 10 toxins found in association with diarrhetic shellfish poisoning: okadaic acid (OA), dinophysistoxin-1 (DTX1), 7-O-palmitoylokadaic acid (palOA), 7-O-palmitoyldinophysistoxin-1 (pa1DTX1), pectenotoxin-1 (PTX1), pectenotoxin-2 (PTX2), pectenotoxin-2 seco acid (PTX2SA), pectenotoxin-6 (PTX6), yessotoxin (YTX), and 45-hydroxyyessotoxin (YTXOH). Toxins in 2 g of the adductor muscle or the digestive glands of scallops, Patinopecten yessoensis, were extracted with 18 ml of methanol-water (9:1, v/v), freed of polar contaminants by partition between chloroform and water, and treated by solid-phase extraction on a silica cartridge column. Samples containing YTXOH were purified separately on a buffered reversed-phase column. Chromatographic separation was achieved by the following combinations of columns and mobile phases: a Symmetry C18 column with acetonitrile-0.05% acetic acid (7:3, v/v) for OA, DTX1, PTX6 and PTX2SA; a Develosil ODS column with the same mobile phase for PTX1 and PTX2; a Capcellpak column with methanol-2.5% acetic acid (98:2, v/v) for palOA and palDTX1; and an Inertsil ODS column with methanol-0.2 M ammonium acetate (8:2, v/v) for YTX and YTXOH. Carboxylic acid toxins were selectively monitored on [M-H]- ions, sulfated toxins on [M-Na]-ions, and neutral toxins on [M+NH4]+ ions. Average recoveries of the toxins spiked to tissue homogenates ranged from 70 to 134%. Detection limits in the muscle ranged from 5 to 40 ng/g and those in the digestive glands from 10 to 80 ng/g.

Chromatography, Liquid↗

Isolation of a new okadaic acid analogue from phytoplankton implicated in diarrhetic shellfish poisoning.

A new analogue of okadaic acid (OA), the toxin mainly responsible for diarrhetic shellfish-poisoning (DSP) phenomena in Europe, has been isolated from toxic phytoplankton (Dinophysis acuta) collected in Irish waters. Fluorimetric LC analyses of the extracts of bulk phytoplankton samples using derivatisation with 9-anthryldiazomethane (ADAM) showed a complex toxin profile, with peaks corresponding to OA and dinophysistoxin-2 (DTX-2) as well as a third unidentified compound. This minor unidentified component was isolated by chromatographic techniques such as normal-phase chromatography, gel permeation on Sephadex, solid-phase extraction and reversed-phase separations. Ionspray mass spectrometry (MS) was used for structural investigation on this compound due to the very small amount of isolated material. Flow injection analysis (FIA)-MS of the isolated compound gave positive-ion mass spectrum dominated by the protonated molecule, [M + H]+, at signal m/z 805, whereas the deprotonated molecule [M - H]- was observed in the negative-ion spectrum at signal m/z 803, thus indicating the molecular weight of 804 for the new toxin, the same as OA and its known isomers, DTX-2 and DTX-2B. Collision-induced dissociation (CID) as obtained by positive and negative tandem mass spectrometry (MS-MS) showed a fragmentation pattern for the new compound which was very similar to that of OA, DTX-2 and DTX-2B. Ionspray microLC-MS of a mixture containing the compound under investigation together with OA analogues showed the compound eluted after OA, DTX-2, DTX-2B and before DTX-1. All the chromatographic and mass spectrometric data indicated the compound to be another OA isomer and it was therefore coded DTX-2C. To the best of our knowledge this is the first report on the isolation of a new compound related to DSP toxins from natural communities of toxic phytoplankton.

Anthracenes↗

Solid-phase extraction and high-performance liquid chromatography procedures for the analysis of paralytic shellfish toxins.

Paralytic shellfish poisoning (PSP) toxins are produced by certain dinoflagellate species such as Gymnodinium catenatum and Alexandrium tamarensis, during certain periods of the year influenced by several environmental factors, affecting the aquaculture industry and mainly bivalve molluscs. HPLC with fluorescence detection is a powerful analytical technique for the analysis of such toxins; several HPLC alternatives have been developed in order to improve the liquid chromatographic analysis, but due to the complexity of the sample matrix, important work has been focused recently on the clean-up of samples prior to HPLC analysis. Solid-phase extraction procedures offer advantages for this clean-up. In this work we focus on the study of three different clean-up methods prior to HPLC with fluorescence detection analysis of PSP toxin present in contaminated mussel samples; by spiking uncontaminated mussel samples with two different PSP toxin standards and by calculating the recovery values for these experiments. These recoveries must be taken into account in order to quantify the exact amount of PSP toxins present in the contaminated samples.

Animals↗

Effects of the diarrhetic shellfish toxin, okadaic acid, on cytoskeletal elements, viability and functionality of rat liver and intestinal cells.

The diarrhetic shellfish toxin, okadaic acid, administered to rats by intragastric intubation, caused intestinal damage, diarrhea and death, but had no detectable effect on the liver. In contrast, okadaic acid administered intravenously had little effect on intestinal function, but caused a rapid dissolution of hepatic bile canalicular actin sheaths, congestion of blood in the liver, hypotension and death at high doses. In isolated rat hepatocytes, okadaic acid induced disruption of the canalicular sheaths as well as of the keratin intermediate filament network. Both of these cytoskeletal changes could be prevented by addition of a cytoprotective flavonoid, naringin, to the isolated hepatocytes, whereas intravenously or intragastrically administered naringin failed to protect against the effects of okadaic acid in vivo. Freshly isolated colonocytes already had fragmented keratin and tubulin cytoskeletons, died rapidly and were not further afflicted by okadaic acid. Naringin had no protective effect on isolated colonocytes or on intestinal function in vivo, but the nonspecific protein kinase inhibitor, K-252a, and the protein-tyrosine-phosphatase inhibitor, vanadate, significantly reduced the extent of colonocytic keratin fragmentation, and an inhibitor of apoptotic caspases, zVAD.fmk, was strongly protective. Further studies of hepatic and intestinal cytoprotectants should focus on conditions that limit their effectiveness in vivo.

Animals↗

Accumulation and depuration of paralytic shellfish poisoning toxins by purple clam Hiatula rostrata Lighttoot.

Purple clams (Hiatula rostrata Lighttoot) accumulated paralytic shellfish poisoning (PSP) toxins produced by a toxic strain of the dinoflagellate Alexandrium minutum Halim for subsequent study of toxin distribution during depuration (detoxification by a nontoxic microalgal diet or starvation). The results confirm the data in the literature concerning the high toxicity of the digestive gland, and the depuration efficiency between feed with nontoxic microalgae and starvation is similar. The toxin profile of the purple clams was similar with that of Alexandrium minutum at the end of the exposure period; GTX4 and GTX1 were dominant. However, at the end of the depuration period, GTX3 and GTX2 were dominant. The non-visceral tissues were toxic after feeding with toxic algae. The toxicity was low and the profile were also similar with that of the toxic algae. No PSP toxins other than GTX-1, 2, 3 and 4 were detected in the experimental period.

Animals↗

Occurrence of paralytic shellfish poison (PSP) in the starfish Asterina pectinifera collected from the Kure Bay, Hiroshima Prefecture, Japan.

Assays were made for paralytic toxicity of marine invertebrates inhabiting at the coasts of Hiroshima Bay, where the infestation of bivalves such as cultured oysters with paralytic shellfish poison (PSP) has been occurred. The starfish Asterina pectinifera collected at the estuary of Nikoh River, Hiroshima Bay, was found to contain moderate levels of paralytic toxicity. Its highest toxicities as PSP found on July 30, 1999 were 12.5 MU/g for whole body, 11.0 MU/g for integument tissues and 3.9 MU/g for viscera, respectively. The toxicity of integument was changed from 3.6 to 11.0 MU/g in 1 year. Its paralytic toxin principles were identified as PSP toxins, composing mainly from saxitoxin (STX) group toxins such as carbamoyl-N-hydroxy neosaxitoxin (hyneoSTX), and STX, by HPLC and LC-MS, accounting for over 90 mol%. The PSP toxins contained in the starfish A. pectinifera considered to be transferred from bivalves or detritus living in the same area, which were contaminated with PSP. However, the involved pathway may be different from that of Asterias amurensis which was infested directly through food chain from its food bivalves, for its toxin pattern.

Animals↗

Identification of a new diarrhoetic toxin in shellfish using liquid chromatography with fluorimetric and mass spectrometric detection.

A new toxin, dinophysistoxin-2B (DTX-2B) was isolated from Irish mussels using silica chromatography, gel permeation, octadecylsilane solid-phase extraction and repeated preparative high-performance liquid chromatography (HPLC). Dinophysistoxin-2 (DTX-2) was also isolated from shellfish using the same procedures. The separation of these toxins in chromatographic fractions was monitored using fluorimetric HPLC following derivatization with 9-anthrylmethyldiazomethane or 1-bromoacetylpyrene. Flow-injection analysis-mass spectrometry (FIA-MS) with an atmospheric pressure ionization (API) and an ionspray (ISP) interface showed a mass spectrum dominated by the protonated molecule, [M+H]+, at m/z 805 for DTX-2B, thus indicating that this new toxin has the same mol.wt as okadaic acid and DTX-2. The low-energy fragment ion spectrum, as produced in FIA-MS experiments by up-front collision-induced dissociation of the protonated molecule of DTX-2B, showed fragment ions corresponding to successive losses of water molecules from the [M+H]+ ion. This low collision energy fragmentation pattern is typical of marine polyether toxins such as okadaic acid, DTX-2 and DTX-1. These results provide strong evidence that DTX-2B is another okadaic acid isomer.

Animals↗

Occurrence of paralytic shellfish poison in the starfish, Asterias amurensis in Kure Bay, Hiroshima Prefecture, Japan.

In May 1996, during surveillance on the toxicity of invertebrates such as bivalves inhabiting the coasts of Hiroshima Bay, the starfish Asterias amurensis collected in the estuary of the Nikoh River was found to contain toxins which showed strong paralytic action in mice; the maximum toxicity (as paralytic shellfish poison, PSP) was 8.0 MU/g for whole body and 28.7 MU/g for viscera throughout the monitoring period, March to July 1996. Attempts were made to identify the paralytic toxins in the starfish. They were extracted with 80% ethanol acidified with acetic acid, followed by defatting with dichloromethane. The aqueous layer obtained was treated with activated charcoal and then applied to a Sep-Pak C18 cartridge. The unbound toxic fraction was analyzed by high-performance liquid chromatography techniques. The starfish toxin was rather unexpectedly identified as PSP. It was comprised of high toxic components (gonyautoxin-1; GTX1, GTX2, GTX3, GTX4, decarbamoyl-GTX3; dcGTX3 and dcSTX) as the major components, which accounted for approximately 77 mole% of all components, along with protogonyautoxin-1, 2, 3 and 4 (PX1-4), which are N-sulfocarbamoyl derivatives. Of the high toxic components, GTX1 was present in the largest amounts. It was concluded that the toxin of starfish collected in the estuary of Nikoh River in May 1996 consisted of PSP, which supposedly came via the food chain from toxic bivalves living in the same area. To our knowledge, this is the first report of the occurrence of PSP in starfish.

Animals↗

Comparative toxicity of the diarrhetic shellfish poisons, okadaic acid, okadaic acid diol-ester and dinophysistoxin-4, to the diatom Thalassiosira weissflogii.

Quantitative structure-activity relationships were determined for the diarrhetic shellfish poisoning (DSP) toxins, okadaic acid (OA), OA diol-ester and dinophysistoxin-4 (DTX-4), using a sensitive bioassay procedure with the diatom Thalassiosira weissflogii. OA diol-ester was found to be nearly as toxic as OA. This result contradicted the accepted idea that only the free acid toxins, such as DTX-1 and OA, are potent phosphatase inhibitors. Postassay analyses using liquid chromatography-mass spectrometry (LC-MS) of cultures incubated with OA diol-ester showed that the ester had partially decomposed to OA, which explained some but not all of the observed toxicity. The formation of OA during the bioassay raised the possibility that cells exposed to inactive DSP toxin esters could metabolically activate them. This was examined in an additional experiment which showed that the hydrolysis of both DTX-4 and OA diol-ester was spontaneous and apparently not mediated by the presence of T. weissflogii cells. However, cells of T. weissflogii challenged with OA diol-ester rapidly metabolized most of the toxin to a more water-soluble product. From interpretation of mass spectral data obtained using ion-spray LC-MS, the metabolite was identified as an oxygenated diol-ester of OA, implying that it was the product of a monooxygenase-detoxification pathway. It is postulated that OA diol-ester, as a lipid-soluble, uncharged molecule with a propensity to hydrolyse to OA, may facilitate the transfer of OA across cell walls and membranes.

Animals↗

Use of a channel biosensor for the assay of paralytic shellfish toxins.

Gonyautoxin (GTX), saxitoxin (STX) and tetrodotoxin (TTX), also known as paralytic shellfish poisons (PSP), block Na+ channels, including those in the frog bladder membrane. A tissue biosensor has been developed, consisting of a Na+ electrode covered with a frog bladder membrane integrated within a flow cell. The direction of Na+ transfer, investigated in the absence of Na+ channel blockers, established that active transport of Na+ occurs across the frogs bladder membrane from the internal to the external face. Transfer was shown to be TTX sensitive. The tissue sensor response to each of the different PSP was recorded and the results compared with toxicities determined by the standard mouse bio-assay. Using high concentrations of TTX from the puffer fish Takifugu niphobles, a linear correlation was found between the results from the two assay systems. However, the tissue biosensor system was also able to detect very low concentrations of TTX in samples from two species of puffer fish (Takifugu niphobles and Takifugu pardalis) at concentrations below the detection limit of the mouse bio-assay.

Animals↗

Butyltins in shellfish, finfish, water and sediment from the Coos Bay estuary (Oregon, USA).

Butyltin was measured in tissue, water and sediment samples collected throughout Coos Bay estuary between 1986 and 1997. Butyltin-induced shell deformation in commercial oysters prompted this assessment. Butyltins are released from tributyltin oxide (TBTO)-containing boat paint. Clams from three sites contained tributyltin (TBT) levels ranging from 168 to 457 microg/kg in 1992-1994. Consequently, Oregon Health Division (OHD) issued a shellfish consumption advisory in 1995; it was rescinded in 1997 after US Environmental Protection Agency (EPA) revised the TBTO oral reference dose (RfD). The revised RfD changed the tissue screening level from 112 to 1120 microg TBT/kg. Fifty percent of sediment samples collected during 1991-1997 and analyzed for total butyltins (TotBT) exceeded the Puget Sound Dredge Disposal Analysis Screening Level (PSDDA SL) of 73 microg TBT/kg dw. TotBT at three shipyards selected for site assessment by EPA ranged from 24 to 68,613 microg/kg dw. Sediment and tissue butyltins have been decreasing in all but one area of the estuary.

Animals↗

The intracellular partitioning of trace metals in marine shellfish.

Marine organisms have evolved a number of metabolic strategies to deal with potentially toxic trace metals. To determine how "detoxification" mechanisms such as metal-binding proteins and concretions are involved in the intracellular partitioning of trace metals in marine shellfish, the oyster, Crassostrea virginica, and the blue crab, Callincetes sapidus, were exposed to controlled levels of trace metals. Oysters accumulated cadmium readily and produced specific low molecular weight, cadmium-binding proteins. Blue crabs produced a single cadmium-binding protein in the hepatopancreas and gills when exposed to cadmium through food or water, respectively. Concretions appear to be of limited importance in detoxification.

Animals↗