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The reactivity of desmosterol and other shellfish- and xanthomatosis-associated sterols in the macrophage sterol esterification reaction.

The acyl-CoA: cholesterol acyl transferase (ACAT) reaction in macrophages is a critical step in atherosclerotic foam cell formation, but little is known about the reaction's sterol substrate specificity. In this report we examine the macrophage ACAT reactivity of the shellfish sterol, desmosterol, and other sterols found in man because of shellfish ingestion or in association with the foam cell diseases sitosterolemia and cerebrotendinous xanthomatosis (CTX). We first show that the J774 macrophage, a foam cell model with a hyperactive ACAT pathway, synthesizes desmosterol instead of cholesterol and that both endogenous and exogenous desmosterol are substrates and stimulators of the ACAT reaction in these cells. When exogenous desmosterol was added to human monocyte-derived macrophages, ACAT was stimulated 29- and 4-fold compared with control and cholesterol-treated cells, respectively. Steryl ester mass accumulation in desmosterol-treated human macrophages was 10-fold greater than in control cells and 3-fold greater than in cholesterol-treated cells. Another shellfish sterol, 24-methylene cholesterol, also stimulated ACAT in human macrophages, but most of the xanthomatosis-related sterols did not stimulate ACAT. These data suggest that: (a) the shellfish sterols desmosterol and 24-methylene cholesterol may be atherogenic; and (b) the excessive foam cell formation seen in sitosterolemia and CTX cannot be explained by ACAT hyperreactivity of their associated sterols.

Animals↗

Clinical and epidemiological features of neurotoxic shellfish poisoning in North Carolina.

BACKGROUND: In October 1987, a red tide due to P. brevis affected the North Carolina coast for the first time. The purpose of our study was to describe the clinical and epidemiological features of neurotoxic shellfish poisoning (NSP), an illness caused by eating shellfish contaminated with the neurotoxins of P. brevis. METHODS: Active surveillance was established for cases of NSP. A descriptive study of the NSP cases was then completed. RESULTS: Forty-eight persons, who had eaten oysters at 20 meals, met the case definition. A variety of gastrointestinal tract and neurological symptoms were reported. The illnesses were generally mild and of short duration, and there were no deaths. Forty-one (85 percent) affected persons lived in five communities located within a 70-kilometer area along the coast. Cases occurred from October 27 to December 9; 27 (56 percent) of the cases occurred before the first closure of affected shellfish waters on November 2. There was a significant increase in the illness attack rate with an increase in the number of oysters eaten. CONCLUSIONS: Routine monitoring of coastal waters for P. brevis is needed to facilitate earlier recognition of red tides, closure of affected areas, and education of the public before substantial exposure to contaminated shellfish occurs.

Adolescent↗

Paralytic shellfish poisoning: post-mortem analysis of tissue and body fluid samples from human victims in the Patagonia fjords.

In July 5, 2002 fishermen working in harvesting sea urchin (Loxechinus albus) in the Patagonia Chilean fjords were intoxicated by consumption of filter-feeder bivalve Aulacomya ater. After the ingestion of 7-9 ribbed mussel, two fishermen died 3-4 h after shellfish consumption. The forensic examination in both victims did not show pathological abnormalities with the exception of the lungs conditions, crackling to the touch, pulmonary congestion and edema. The toxic mussel sample showed a toxicity measured by mouse bioassay of 8575 microg of STX (saxitoxin) equivalent by 100 g of shellfish meat. Using post-column derivatization HPLC method with fluorescent on line detection was possible to measure mass amount of each paralytic shellfish poisoning (PSP) toxin yielding individual toxin concentrations. These PSP toxins were identified in the gastric content, body fluids (urine, bile and cerebrospinal fluid) and tissue samples (liver, kidney, lung, stomach, spleen, heart, brain, adrenal glands, pancreas and thyroids glands). The toxin profiles of each body fluid and tissue samples and the amount of each PSP toxin detected are reported. The PSP toxins found in the gastric content, were STX and the gonyautoxins (GTX4, GTX1, GTX5, GTX3 and GTX2) which showed to be the major amount of PSP toxins found in the victims biological samples. The PSP toxin composition in urine and bile showed as major PSP toxins neoSaxitoxin (neoSTX) and GTX4/GTX1 epimers, both STX analogues with an hydroxyl group (-OH) in the N(1) of the tetrahydropurine nucleus. The neoSTX was not present in the gastric content sample, indicating that the oxidation of N(1) in the STX tetrahydropurine nucleus resulted neoSTX, in a similar way that GTX3/GTX2 epimers were transformed in GTX4/GTX1 epimers. Beside this metabolic transformation, also the hydrolysis of carbamoyl group from STX to form its decarbomoyl analogue decarbamoylsaxitoxin was detected in liver, kidney and lung. These two findings show that PSP toxins went under metabolic transformation during the 3-4 h of human intoxication period, in which PSP toxins showed enzymatic oxidation of N(1) in the tetrahydropurine nucleus, producing neoSTX and GTX4/GTX1 epimers starting from STX and GTX3/GTX2 epimers, respectively. This study conclude, that PSP toxins are metabolically transformed by humans and that they are removed from the body by excretion in the urine and feces like any other xenobiotic compound.

Animals↗

Occurrence of paralytic shellfish poison (PSP)-producing dinoflagellate Alexandrium tamarense in Hiroshima Bay, Hiroshima Prefecture, Japan, during 1993-2004 and its PSP profiles.

To assess levels of shellfish intoxication by the paralytic shellfish poison (PSP)-producing dinoflagellate Alexandrium tamarense, potential health risks to human shellfish consumers and the possible need for regulatory intervention, yearly variations of maximum cell density of this species were examined from 1993 to 2004 in Kure Bay and Kaita Bay, which are located within Hiroshima Bay, Hiroshima Prefecture, Japan. The seawater temperature was determined concomitantly. In Kure Bay, maximum concentrations of 1,400 and 1,300 cells/mL at 0 and 5 m depths were observed on 21 and 24 April 1997. In Kaita Bay, remarkably high concentrations above 1,000 cells/mL of A. tamarense were observed in two out of three years investigated. These facts suggest that the environment in both bays is favorable for the propagation of A. tamarense. The temperature range at which the natural population of A. tamarense blooms was generally from 12 to 16 degrees C. Four strains (ATKR-94, -95, -97 and -01) from Kure Bay and one strain (ATKT-97) from Kaita Bay were established. The strain ATKR-94, cultured in modified SW-2 medium at 15 degrees C for 15 days, showed a specific toxicity of 33.8 x 10(-6) MU/cell. The toxins in all five strains exist almost exclusively as beta-epimers (C2 (PX2 or GTX8), GTX3, dcGTX3 and GTX4), which accounted for 54.9 to 73.0 mol% of the total. The corresponding a-epimers (C1 (PX1 or epi-GTX8), GTX2, dcGTX2 and GTX1) accounted for 6.0 to 28.9 mol%. The toxin profiles of ATKR-97 and ATKT-97 were characterized by unusually high proportions of low-potency sulfocarbamoyl toxin, which comprised 62.4 and 68.2 mol%, respectively, of total toxins. In the toxic bivalves, the low-toxicity sulfocarbamoyl components, major components of A. tamarense, were present in amounts of only a few percent, suggesting that in vivo conversion of PSP occurs after ingestion. A comparison of the toxin profiles of the causative dinoflagellate and contaminated bivalves showed that PSP components exist in the bivalves in the form of alpha-epimers, presumably owing to accumulation or storage of the toxins.

Animals↗

Shellfish and public health: a Swedish perspective.

Bivalves are ancient animals that feed by filtering large volumes of water. In this way, phytoplankton, bacteria and viruses from the water column are greatly concentrated in the mussels. The hazards associated with the consumption of mussels are thus dependent on the occurrence and composition of toxic algae and human microbial pathogens in the areas where shellfish are grown. Diarrheic shellfish toxins have occurred regularly in Sweden during the past 27 years. Peaks of toxins in mussels are mostly recorded from October to December, but the pattern can differ significantly due to location and year, making it hard to predict toxin levels in mussels. With an expansion of aquaculture and a subsequent increase in seafood consumption, better risk management is needed to minimize the effects on humans of algal toxins and human pathogens. New control strategies that have to be implemented are: i) proper site selection of culture installations; ii) regular and cost-efficient monitoring of algae, bacteria and viruses; iii) new indicators for fecal contamination, suitable for the specific locations where shellfish grow; iv) rapid dissemination of information to the industry and public, including risk assessment and advice on how to cope with the situation.

Animals↗

Paralytic shellfish poisoning in Singapore.

Paralytic shellfish poisoning is caused by the ingestion of shellfish meat rendered toxic by exposure to a high level of toxic dinoflagellates during the phenomenon of "red tide". This paper reports the first outbreak of paralytic shellfish poisoning from green mussels in Singapore which resulted in two deaths. Analysis of the mussel meat by a standardised mouse bioassay confirmed the presence of the toxin. An attempt was also made to extend the bioassay to an analysis of the gastrointestinal contents. The clinical features of the condition are presented.

Animals↗

Measurements of paralytic shellfish poisons. A review of biological and chemical procedures.

Paralytic shellfish poisons (PSP) are derivatives of a tetrahydropurine base, which includes saxitoxin, 1-hydroxy saxitoxin, and 11-hydroxy saxitoxin sulfate. These compounds are produced by Gonyaulax catenella and other dinoflagellate species, and the algal toxins (phycotoxins) contaminate shellfish during the filter-feeding process performed by the bivalve molluscs. Increased incidence of algal blooms and outbreaks of PSP food poisonings have been encountered in recent years, resulting in a demand for closely monitoring of shellfish for these toxins. The existing biological and chemical procedures for analysis are reviewed. The mouse bioassay is commonly used in routine analysis, but is nonspecific. Several of the chemical procedures are specific and more sensitive than the mouse bioassay. The disadvantage, however, seems to be that not all known PSP compounds can be quantitiatively measured by any single chemical procedure.

Animals↗

Shellfish-borne illnesses. A Hong Kong perspective.

This article provides an overview of the spectrum of infectious and toxic illnesses that may occur following the consumption of contaminated shellfish in Hong Kong. These include hepatitis A, hepatitis E, infections due to vibrio species, paralytic shellfish poisoning, neurotoxic shellfish poisoning and heavy metal poisoning. Possible preventive measures are discussed.

Adolescent↗

Isolation and purification procedures for the preparation of paralytic shellfish poisoning toxin standards.

Paralytic shellfish poisoning (PSP) is caused by mixtures of saxitoxin analogs of which more than eighteen are known. Reliable and sensitive analytical methods and assays for these toxins are essential to protect the consumer and the shellfish industry, but research has been restricted by a shortage of the pure compounds. Only saxitoxin has so far been generally available as a PSP toxin standard, yet sulfated analogs usually occur in higher concentrations than saxitoxin in toxic marine algae and shellfish. Methods are described for the purification of some of the common PSP toxins, in quantities sufficient for the preparation of PSP standards from the dinoflagellate Alexandrium excavatum, the giant sea scallop (Placopecten megallanicus) hepatopancreas, and the cyanobacterium Aphanizomenon flos-aquae. Purity was monitored by high performance liquid chromatography with fluorescence detection (HPLC-FD), ionspray mass spectrometry (ISP-MS), capillary electrophoresis (CE), and proton NMR spectroscopy.

Animals↗

Ecological analysis of digestive cancer mortality related to contamination by diarrhetic shellfish poisoning toxins along the coasts of France.

Shellfish consumers are exposed to the risk of diarrhea from, among other contaminants, algae that produce diarrhetic shellfish poisoning (DSP) toxins, such as Dinophysis spp. These illnesses have been effectively prevented since 1984, when a phycotoxin monitoring network was set up along the coasts of France. There is nonetheless concern that residual levels of okadaic acid, a known tumor promoter that is the main toxin present in French coastal waters, might increase the risk of cancer among regular shellfish consumers. To test this hypothesis, we conducted an ecological study linking digestive cancer mortality rates with a proxy measure of contamination by DSP toxins in 59 coastal areas. Observed and expected numbers of deaths (using national rates as the reference) were computed by sex, cause of death, and area for two time periods: 1984-1988 and 1989-1993. The level of contamination in each area was estimated by the total number of weeks since monitoring began that production was shut down because of DSP toxin contamination. Using both Poisson regressions and test for trends of standardized mortality ratios across four exposure categories, we found some evidence of associations for several digestive cancer sites (esophagus, stomach, colon, liver, and total digestive cancers for men; stomach and pancreatic cancers for women). Among men, the only statistically significant result that remained after taking possible confounding by alcohol use into account involved colon cancer. The conclusions provided by this analysis are very tentative; they need to be reproduced and interpreted in the light of additional information on the potential long-term effects of DSP toxins. In the absence of human data, they provide some indication of a possible association between exposure to DSP toxins and digestive cancers.

Adult↗

Determination of petroleum contamination in shellfish using solid phase micro-extraction with gas chromatography-mass spectrometry.

Headspace solid phase micro-extraction (HS-SPME) has been applied as a sampling technique for the determination of petroleum contamination in shellfish using capillary gas chromatography-mass spectrometry (GC-MS). A poly(dimethylsiloxane) fused silica fibre (100 microm thickness) was found to be satisfactory for the extraction of a range of aliphatic hydrocarbons (HCs) from homogenised shellfish tissues. The SPME conditions, including temperature, salt content, extraction time and desorption temperature, were optimised for a range of aliphatic HCs (C9-C20). A methyl silicone column GC (12 m x 0.20 mm, 0.33 microm layer thickness) was used with a temperature programme from 40 to 260 degrees C and the HCs were determined within a mass range of m/ z=50-550 in electron impact mode. Calibration range was from 10 to 5000 ng/g with linear correlation coefficients ( r(2)) of 0.982 for nonane to 0.997 for octadecane. Detection limits for aliphatic HCs, spiked into shellfish (mussel) tissues, varied from 3.6 ng/g (tetradecane) to 51 ng/g (eicosane) and relative standard deviation (% RSD) values ranged from 1.4% (hexadecane) to 24.3%(eicosane).

Animals↗

Shellfish conflict in Baynes Sound: a strategic perspective.

The shellfish aquaculture industry (SAI) has operated in Baynes Sound, British Columbia (BC) since the early 1900s. Recognizing the economic potential of the area, the industry has requested additional farming opportunities. However, Baynes Sound upland residents and many other stakeholders have expressed concerns that SAI activities are having a negative impact on the environment, quality of life, and other nonaquaculture resource uses in the area. In order to address these issues, the Action Plan was initiated by a BC government interagency project team in November 2001. To assist in assessing the strategic aspects of this conflict, the decision support system GMCR II is employed here to apply a new methodology, the graph model for conflict resolution, to systematically analyze the ongoing conflict over shellfish aquaculture development in Baynes Sound within a social, economic, and environmental framework. Valuable insights are procured to guide decision-makers toward sustainability of the shellfish industry.

Animals↗

Determination of oxytetracycline in marine shellfish (Crassostrea gigas, Ruditapes philippinarum and Scrobicularia plana) by high-performance liquid chromatography using solid-phase extraction.

A reversed-phase high-performance liquid chromatographic method was developed to detect oxytetracycline (OTC) in three species of marine shellfish (Crassostrea gigas, Ruditapes philippinarum and Scrobicularia plana). Shellfish tissues were analysed after solid-phase extraction by using a mobile phase containing acetonitrile and 0.02 M orthophosphoric acid solution. The linearity and precision of the method were checked over the concentration range 0.100-1.500 micrograms/g. The limits of detection and determination of OTC were 0.040 and 0.100 microgram/g, respectively. The recovery of OTC from spiked shellfish tissues was 79.8%. The OTC concentration in oyster (Crassostrea gigas) spiked at 0.500 microgram/g and stored at -20 degrees C was stable for 6 weeks. The method was applied to a 21-day experimental study performed with oysters.

Animals↗

Paralytic shellfish poisons produced by the freshwater cyanobacterium Aphanizomenon flos-aquae NH-5.

A single filament clonal isolate of Aphanizomenon flos-aquae was made from a water bloom sample taken at a small pond near Durham, New Hampshire, in 1980. When batch cultured the strain was toxic to mice and had an i.p. LD50 of about 5.0 mg/kg. Using an extraction procedure originally designed for paralytic shellfish poisons and other neurotoxins of freshwater cyanobacteria, a purification method was developed. The procedure involved acidified water/ethanol extraction of the cells followed by ultrafiltration, gel filtration, use of C18 cartridges to remove pigments, ion-exchange and high performance liquid chromatography using u.v. detection at 220 or 240 nm. Thin-layer chromatography and high performance liquid chromatography results indicate that Aphanizomenon flos-aquae NH-5 may produce paralytic shellfish poisons, mainly neo-saxitoxin and saxitoxin. Three labile toxins were also detected which were not similar to any of the known paralytic shellfish poisons.

Animals↗

Patterns of experimental contamination by Protogonyaulax tamarensis in some French commercial shellfish.

As a result of the proliferation of toxic marine dinoflagellates along European coasts and the recent discovery of paralytic poisons in French shellfish, experimental studies were conducted on four species of shellfish from the Brittany coasts. Contamination rates of a culture of toxic Protogonyaulax tamarensis, were determined for Mytilus edulis, Crassostrea gigas, Pecten maximus and Ruditapes philippinarum. Mussels and scallops were very rapidly contaminated showing high toxin accumulation rates, whereas rates for oysters and clams were low. During the decontamination phase, two stages were observed in mussels and scallops: a fast decrease in toxin, of the same order of magnitude as the accumulation, followed by a slow decrease, with the toxic rate remaining above the quarantine level of 80 micrograms/100 g. Toxin analysis, both in the culture and in the shellfish, was performed using high performance liquid chromatography. GTX3 and GTX8/epiGTX8 were the dominant toxins in the early stage of the decontamination phases, whereas GTX2 was the predominant compound during the slow phase of decontamination.

Animals↗

Paralytic shellfish poison (saxitoxin family) bioassays: automated endpoint determination and standardization of the in vitro tissue culture bioassay, and comparison with the standard mouse bioassay.

Mouse neuroblastoma cells swell and eventually lyse upon exposure to veratridine, which, when added together with ouabain, enhances sodium ion influx. In the presence of saxitoxin (STX), which blocks sodium channels, the action of the other two compounds is inhibited and the cells remain morphologically normal. A tissue culture bioassay using mouse neuroblastoma cells, developed by Kogure and colleagues, takes advantage of these principles; in this bioassay, the fraction of the cells protected from the actions of ouabain and veratridine is in direct proportion to the concentration of STX and its analogues. We have modified this bioassay, improving its convenience and speed by eliminating the need to count individual cells to determine the saxitoxin equivalents, and instead have employed a microplate reader for automated determinations of absorbances of crystal violet from stained neuroblastoma cells. When these changes and other minor technical modifications were tested in the tissue culture bioassay systematically, we found the lower detection limit to be around 10 ng STX equivalents (eq) per ml of extract ( = 2.0 micrograms STX eq/100 g shellfish tissue). Our version of the tissue culture bioassay was compared with the standard mouse bioassay using 10 acid extracts of dinoflagellates (Alexandrium excavata and A. fundyense) and 47 AOAC extracts of shellfish tissues. The tissue culture bioassay provided results virtually identical to those obtained with the mouse bioassay (r > 0.96), and moreover, was considerably more sensitive. The results gained from high performance liquid chromatographic (HPLC) analysis of 12 of the same extracts were less consistent when compared with the results from both bioassay methods. The automated tissue culture (neuroblastoma cell) bioassay may be a valid alternative to live animal testing for paralytic shellfish poisoning.

Animals↗

Dinophysistoxin-2: the predominant diarrhoetic shellfish toxin in Ireland.

Diarrhoetic shellfish poisoning (DSP) in Europe is due mainly to the presence of the dinoflagellate toxin, okadaic acid (OA). However, analysis of cultivated mussels (Mytilus edulis) from southwest Ireland revealed that an isomer of OA, dinophysistoxin-2, was the major toxin present during DSP episodes. Using fluorimetric HPLC, following derivatisation with 9-anthryldiazomethane, both OA and DTX-2 were found in shellfish during a prolonged toxic episode in 1991. However, examination of similar mussel cultivation locations in 1994 showed that DTX-2 was even more predominant. During this DSP period, OA levels were less than 0.7 microgram/g, whereas maximum DTX-2 levels of 6.3 micrograms/g hepatopancreas were recorded. This toxicity in shellfish occurred soon after high cell counts of Dinophysis acuta were observed. As well as large seasonal variability in toxin levels in rope cultured mussels, substantial variations were also observed, both horizontally and vertically, within the water column.

Animals↗

Plutonium and americium uptake in rats fed with Cumbrian shellfish--implications for estimates of dose to man.

Winkles (Littorina littorea) and mussels (Mytilus edulis) collected on the Cumbrian coast contain americium-241 and isotopes of plutonium discharged from the nuclear-fuel reprocessing plant at Sellafield. Shellfish have been fed to rats and measurements made of the gastrointestinal absorption of the actinides. For shellfish collected over a 1-year period from March 1983 to February 1984, the average values for the fractional absorption of plutonium and americium were 9 x 10(-4) and 3 x 10(-4), respectively, for winkles and 1.5 x 10(-3) and 6 x 10(-4), respectively, for mussels. Comparisons with results for winkles collected in December 1981 and mussels collected in July 1982 suggest that there may be considerable seasonal variation in the availability of the actinides for absorption. The results suggest that in calculations of doses to individuals consuming shellfish in west Cumbria, it may be prudent to examine the effect of using the new ICRP gut transfer factor of 1 x 10(-3) for both actinides, in comparison with the value of 5 x 10(-4) recommended previously by NRPB. The use of 1 x 10(-3) would increase the estimate of the committed effective dose equivalent for 1985 intakes, from the value of 0.73 mSv calculated by the Ministry of Agriculture, Fisheries and Food, to 1.29 mSv. However, taking into account up-to-date estimates of the retention of the actinides in liver and bone would reduce this value to 1.07 mSv. If, in addition, allowance is made for the effect of the burial and recycling of actinides in bone, a significant reduction in the dose estimate could result; for example, the use of one proposed dynamic bone model would reduce the value from 1.07 to 0.54 mSv.

Americium↗