Development of a protocol for determination of domoic acid in the sand crab (Emerita analoga): a possible new indicator species.

The aim of this study was to begin evaluating the utility of sand crabs (Emerita analoga) as an indicator species for the algal neurotoxin, domoic acid (DA), in Monterey Bay, California, USA, a site of recurrent blooms of the DA-producing diatom, Pseudo-nitzschia. One of the current sentinel organisms, the sea mussel (Mytilus californianus), has shown minimal or undetectable toxicity during some local bloom events. As a critical step in assuring the accuracy of DA determinations in E. analoga, we have developed and validated a highly efficient extraction protocol that yields toxin recoveries of 97+/-2.9%. We also determined by HPLC-UV and receptor binding assay, with confirmation by LC-MS/MS, that sand crabs accumulated measurable amounts of DA during toxic Pseudo-nitzschia blooms, while the sea mussel showed no detectable toxin. In addition, a comparison of inter-animal variability in DA content revealed values ranging from ca. 0.5 to 5 microg DAg(-1) tissue and no consistent trend with size class, based on either animal weight or length. These data on the toxicity of individual animals will be useful in designing an appropriate sampling strategy for monitoring DA and, importantly, indicate that sand crabs do not appear to progressively bioaccumulate DA with age.     

Uptake, tissue distribution and excretion of domoic acid after oral exposure in coho salmon (Oncorhynchus kisutch)

Domoic acid (DA) is a potent neurotoxin naturally produced by some pennate diatom species of the genus Pseudo-nitzschia. It is well known that during harmful algal blooms fish can accumulate DA in the gastrointestinal (GI) tract and act as vectors of the toxin to higher trophic level piscivores, often with severe neurotoxic consequences to the predators. Although neurotoxicity and mass mortality have been observed in vertebrates (i.e. marine mammals and sea birds) feeding on contaminated fish, to date there has been no evidence of neurobehavioral toxicity in the fish vectors themselves. It has been hypothesized that fish may not absorb DA from the digestive tract, thus making them insensitive to dietary consumption of DA. To test this hypothesis, we performed oral gavage exposures followed by a time series of tissue dissections to characterize uptake, depuration, and tissue distribution of DA in fish. Intracoelomic (IC) injection exposures (which bypass the GI tract) were also performed to determine if coho neurons are neurologically susceptible to DA. Excitotoxic symptoms were observed in fish via IC injection at similar toxin levels that have been reported to induce excitotoxic symptoms in intraperitoneal (IP) exposures with mammalian models such as mice, suggesting that fish neurons have a similar sensitivity to DA as other vertebrates. Surprisingly, after oral gavage with ecologically relevant doses of DA, the toxin was detected in plasma collected from the dorsal aorta via a permanent intraarterial catheter within 15 min, yet excitotoxic symptoms were not observed. Additionally, DA was detected in liver, heart, spleen, kidney, muscle, brain and bile. These data indicate that although DA is absorbed from the gut, fish do not exhibit neuroexcitatory effects at maximum ecologically relevant oral doses of DA. Tissue distribution and DA uptake and depuration patterns suggest that a majority of the absorbed toxin is excreted via the kidneys and bile, thereby preventing toxic levels of DA from reaching sensitive nervous tissue. Additionally, greater than 20% of total IC administered DA doses were sequestered in bile within 1h of injection in five symptomatic fish, providing evidence for biliary sequestration of the toxin from blood. Here, we comprehensively describe the uptake, depuration, and tissue distribution patterns of DA and propose that renal and biliary processes may serve as primary routes of toxin clearance in fish.     

In vivo genotoxicity testing of the amnesic shellfish poison (domoic acid) in piscine erythrocytes using the micronucleus test and the comet assay

Domoic acid (DA) is a neurotoxic amino acid naturally produced in the marine environment by some diatom species belonging to the genus Pseudo-nitzschia. Although the neurotoxic properties of DA have been demonstrated, very little is known about in vivo genotoxicity of DA on aquatic organisms. In the present paper, an in vivo study on the genotoxic effects of domoic acid was carried out on a fish, Oreochromis niloticus, using the micronucleus test and the comet assay. The fish were exposed to three doses of domoic acid (1, 5 and 10 microg/g body weight) by intracoelomic injections. Ethyl methane sulphonate at a single dose of 5mg/l was used as positive control. Analysis of micronuclei, nuclear abnormalities and DNA damage were carried out on peripheral erythrocytes sampled 24, 48 and 72 h post-treatment. Our results revealed significant increases in the frequencies of micronuclei, nuclear abnormalities as well as DNA strand breaks and thus demonstrated the genotoxic potential of DA on fish.     

Accumulation, transformation and tissue distribution of domoic acid, the amnesic shellfish poisoning toxin, in the common cuttlefish, Sepia officinalis

Domoic acid (DA) is a phycotoxin produced by some diatoms, mainly from the Pseudo-nitzschia genus, and has been detected throughout the marine food web. Although DA has been frequently found in cephalopod prey such as crustaceans and fish, little is known about DA accumulation in these molluscs. This study presents the first data showing relevant concentrations of DA detected in the common cuttlefish, Sepia officinalis, which is one of the most studied cephalopod species in the world. Domoic acid was consistently found throughout 2003 and 2004 in the digestive gland of cuttlefish reaching concentrations of 241.7 microg DA g(-1). The highest DA values were detected during spring and summer months, periods when Pseudo-nitzschia occur in the plankton. In fact, Pseudo-nitzschia blooms preceded the highest DA concentrations in cuttlefish. Evaluation of DA tissue distribution showed elevated DA concentrations in the digestive gland and branchial hearts. Further, DA isomers comprised a relevant percentage of the toxin profile, indicating degradation and biotransformation of the toxin in the branchial hearts. The common cuttlefish, like other cephalopod species, plays a central position in the food web and might be a new DA vector to top predators like marine mammals. Human intoxications are not expected since DA was only seldom detected in the mantle and even then in very low levels (max 0.7 microg DA g(-1)). However, in some countries whole juvenile animals are consumed (i.e. without evisceration) and in this case they might represent a risk to human health. This study contributes to understanding the occurrence of phycotoxins in cephalopods and reveals a new member of the marine food web able to accumulate DA.     

Domoic acid accumulation in French shellfish in relation to toxic species of Pseudo-nitzschia multiseries and P. pseudodelicatissima.

Within the French phytoplankton monitoring network (REPHY), domoic acid (DA), the toxin responsible for amnesic shellfish poisoning, was first detected in samples collected in 1998. Toxin analysis by the official method [liquid chromatography with diode array detection (LC/DAD)] was performed when Pseudo-nitzschia cell concentration was greater than 1.0 x 10(5) cells/l. LC/DAD results obtained in 1999 and 2000 showed increased DA accumulation in bivalves sampled at different sites along French coasts. The toxin maximum in 1999 was 3.2 microg DA/g of whole tissue, whereas the levels in 2000 (53 microg) were above the sanitary threshold (20 microg DA/g tissue). Phytoplankton samples collected during blooms were observed by both light and scanning electron microscopy (SEM). Identification of phytoplankton species by SEM analyses confirmed the presence of two known DA-producing species, P. pseudodelicatissima and P. multiseries. LC/DAD results for a mass culture of P. multiseries indicated that this species was involved in DA accumulation in French shellfish.     

Dynamics of microcystins in the mussel Mytilus galloprovincialis.

The accumulation and depuration of hepatotoxins produced by the freshwater cyanobacterium Microcystis aeruginosa in the mussel Mytilus galloprovincialis was studied. Mussels were fed daily 10(5) cells/ml of the toxic cyanobacterium that produces microcystin-LR (MCYST-LR), for four days. After that period animals were placed in toxin free water and were fed the diatom Nitzschia sp. During two weeks the concentration of the toxin in the mussels, as also in their feces and in the water where animals were placed individually during 24 h, were monitored using an ELISA assay. No mussel mortality was registered during the whole experiment. Mussels showed a maximum detectable level of MCYST of 10.7 microg/g mussels dry weight (DW) during the accumulation period, rising to 16.0 microg MCYST/g mussel DW by day two of the depuration period. Then there was a decrease trend with peaks of toxin at days 6, 8, 11 and 14. The rise of the toxin level on day two of the depuration period seems to have been due to the reingestion of contaminated feces. In fact, feces showed high amounts of MCYST during the first days of depuration with a maximum of 140 microg/d DW on day 3. This coincided with a 50% decrease on the detectable toxin in the mussels reflecting the emptiness of their digestive tract. In the water the highest level of the toxin was 2.5 microg MCYST/liter and some toxin peaks were also observed during the depuration period. This fluctuation of the toxin levels in the mussels, feces and water may be related to the renewal of protein phosphatases and subsequent release of unbound toxins. Results show that depuration of MCYST by mussels is not a very rapid process and contamination by feces containing MCYST is likely to occur and increase the persistence of these toxins in the mussels after the bloom disappearance. Monitoring programs for harmful algal blooms usually include only toxic dinoflagellates and diatoms and their toxins in bivalves. Taken into account the present work they should also include hepatotoxins from cyanobacteria, namely in brackish waters such as estuaries of eutrophic rivers in order to avoid human health hazard.     

Confirmation of domoic acid production of Pseudo-nitzschia multiseries isolated from Ofunato Bay, Japan.

Production of domoic acid (DA), the responsible toxin for amnesic shellfish poisoning, was examined for 44 strains of Pseudo-nitzschia spp. isolated from Ofunato Bay, Japan. Only one strain which was identified as Pseudo-nitzschia multiseries produced DA in a level comparable to Canadian strains. No significant DA was detected in the rest of the strains, indicating that toxic P. multiseries does not bloom in a high density in the bay.     

Exposure to domoic acid affects larval development of king scallop Pecten maximus (Linnaeus, 1758)

Domoic acid (DA) is a highly toxic phycotoxin produced by bloom forming marine diatoms Pseudo-nitzschia spp. Bivalves can accumulate this toxin to a high level through their feeding activities, and thus illness or death in can occur in consumers of bivalves. In this study, king scallop, Pecten maximus, larvae were exposed to dissolved domoic acid (DA) for 25d, and the toxin accumulation and effects of harbouring this toxin were investigated. Scallop larvae incorporated DA continuously during the larval culture period and accumulated a maximum DA level of 5.21pgind(-1) when exposed to a solution of 50ngml(-1) dissolved DA. As a result of the DA treatment, larval growth, measured in terms of shell length and the appearance of the eye-spot, and larval survival were significantly compromised. This is the first study on DA incorporation dynamics in P. maximus larvae, signifying the potential of using shellfish larvae for the study on mechanisms of phycotoxin accumulation. The negative effect of DA exposure suggests that this toxin could possibly influence natural recruitment in P. maximus, and it may be necessary to protect hatchery-cultured scallop larvae from DA during toxic Pseudo-nitzschia blooms.     

Emerita analoga (Stimpson)--possible new indicator species for the phycotoxin domoic acid in California coastal waters.

Blooms of domoic acid (DA) synthesizing diatoms (Pseudo-nitzschia spp.) have been associated with the death and injury of hundreds of marine shorebirds and mammals, exposed humans to potentially serious health risks, and threatened to significantly impact coastal fisheries and commerce dependent on marine resources. While indicator organisms are widely utilized to monitor for marine biotoxins like paralytic shellfish poisoning toxins, a reliable intertidal indicator species to monitor DA remains to be identified. Here we evaluate and confirm the utility of the common sand crab (Emerita analoga) as an indicator for DA in comparison with sea mussels (Mytilus californianus). Mussels and sand crabs, collected from natural populations in Santa Cruz, California (April 1999-February 2000), were tested for DA using the HPLC-UV method. Toxin loads in sand crabs ranged from below detectable limits to 13.4 micro g DA g(-1) and coincided with the abundance of DA producing Pseudo-nitzschia species nearshore. Toxin levels in mussels collected during the study period were below HPLC-UV detectable limits. The rise and fall of DA in sand crabs in synchrony with Pseudo-nitzschia abundance, combined with this common intertidal species' accessibility and ease of DA extraction, clearly indicate the utility of sand crabs as a reliable, cost-effective monitoring tool for DA in the nearshore coastal environment.     

Microcystin accumulation in liver and muscle of tilapia in two large Brazilian hydroelectric reservoirs.

The objective of this study was to measure levels of the toxin microcystin in different tissues of fish known to feed on cyanobacteria during toxic bloom events. Wild Nile and redbreast tilapia (Oreochromis niloticus and Tilapia rendalli) were sampled from the catch of artisanal fishermen at eutrophic stations of Funil and Furnas reservoirs in southeastern Brazil. Phytoplankton communities in the two reservoirs were quite different taxonomically, but not dissimilar in microcystin content (200 microg g dry weight (DW) seston(-1) at Funil, 800 microg gDW seston(-1) at Furnas). All of the 27 fish sampled contained microcystin, ranging from 0.8 to 32.1 microg g liver(-1) and from 0.9 to 12.0 ng g muscle(-1). Most microcystin variants found in seston were also found in fish liver. T. rendalli had the lowest concentration in both tissues when compared to O. niloticus. In both reservoirs, one of every four fish sampled, always O. niloticus, had a level of microcystins beyond the World Health Organization tolerable daily intake (8 ng g tissue(-1)) and represented a risk for consumers. It is possible that closer study of inter-species variability in toxin burden in cyanobacteria-impacted water bodies will permit the development of guidelines for fish consumption that will better protect public health.     

A potential vector of domoic acid: the swimming crab Polybius henslowii Leach (Decapoda-brachyura).

The swimming crab Polybius henslowii may play an important role in the movement of the amnesic shellfish toxin, domoic acid (DA), through the marine food chain. High DA concentrations have been determined in crab samples harvested along the Portuguese coast during the summer of 2002, reaching a level of 323.1 microg DA/g crab tissue. Toxin distribution in the different crab organs showed levels as high as 571.6 microg DA/g in the visceral tissues. Levels of toxin 4-12 times lower were detected in the remaining tissues. This crab might be a prominent vector of the toxin to higher trophic levels, including fishes, sea birds and even humans. In Portugal P. henslowii is commercialised during the summer in some local markets. DA concentrations were found close to the legal limit of 20 microg/g in samples purchased at Figueira da Foz market. The crabs are boiled prior to reaching the consumers. The cooking process was evaluated. Determination of toxin losses during the cooking process showed a toxin reduction higher than 50%. DA was determined by HPLC-UV and confirmed by spectra acquired with diode-array detector.     

Spatio-Temporal Monitoring of Benthic Anatoxin-a-Producing Tychonema sp. in the River Lech,Germany

Incidents with toxic benthic cyanobacteria blooms have been increasing recently. In 2019, several dogs were poisoned in the river Lech (Germany) by the benthic anatoxin-a-producing genus Tychonema. To characterize spatial and temporal distribution of potentially toxic Tychonema in this river, a systematic monitoring was carried out in 2020, focusing on the occurrence of the genus, its toxin production and habitat requirements. Tychonema and cyanobacterial community composition in benthic mats and pelagic samples were identified using a combined approach of microscopy and DNA sequencing of the 16S rRNA gene. In addition, anatoxin-a concentrations of selected samples were measured using the ELISA method. The habitat was characterized to assess the ecological requirements and growth conditions of Tychonema. Tychonema mats and anatoxin-a were detected at several sampling sites throughout the entire study period. Toxin concentrations increased with the progression of the vegetation period and with flow direction, reaching values between 0 and 220.5 µg/L. Community composition differed among pelagic and benthic samples, with life zone and substrate condition being the most important factors. The results of this study highlight the importance of monitoring and understanding the factors determining occurrence and toxin production of both pelagic and benthic cyanobacteria due to their relevance for the health of humans and aquatic ecosystems.     

Cytochrome P4501A1 expression in blubber biopsies of endangered false killer whales (Pseudorca crassidens) and nine other odontocete species from Hawai‘i

Odontocetes (toothed whales) are considered sentinel species in the marine environment because of their high trophic position, long life spans, and blubber that accumulates lipophilic contaminants. Cytochrome P4501A1 (CYP1A1) is a biomarker of exposure and molecular effects of certain persistent organic pollutants. Immunohistochemistry was used to visualize CYP1A1 expression in blubber biopsies collected by non-lethal sampling methods from 10 species of free-ranging Hawaiian odontocetes: short-finned pilot whale, melon-headed whale, pygmy killer whale, common bottlenose dolphin, rough-toothed dolphin, pantropical spotted dolphin, Blainville’s beaked whale, Cuvier’s beaked whale, sperm whale, and endangered main Hawaiian Islands insular false killer whale. Significantly higher levels of CYP1A1 were observed in false killer whales and rough-toothed dolphins compared to melon-headed whales, and in general, trophic position appears to influence CYP1A1 expression patterns in particular species groups. No significant differences in CYP1A1 were found based on age class or sex across all samples. However, within male false killer whales, juveniles expressed significantly higher levels of CYP1A1 when compared to adults. Total polychlorinated biphenyl (∑PCBs) concentrations in 84 % of false killer whales exceeded proposed threshold levels for health effects, and ∑PCBs correlated with CYP1A1 expression. There was no significant relationship between PCB toxic equivalent quotient and CYP1A1 expression, suggesting that this response may be influenced by agonists other than the dioxin-like PCBs measured in this study. No significant differences were found for CYP1A1 expression among social clusters of false killer whales. This work provides a foundation for future health monitoring of the endangered stock of false killer whales and other Hawaiian odontocetes.     

Developmental toxicity of domoic acid in zebrafish (Danio rerio)

Domoic acid (DA) is a rigid analog of the excitatory amino acid glutamate. It is produced by the diatom genus Pseudo-nitzschia and is a potent neurotoxin in both adult and developing animals. We have used zebrafish (Danio rerio) as a model to investigate and characterize the developmental toxicity of DA. Domoic acid was administered by microinjection to fertilized eggs at the 128- to 512-cell stages in concentrations ranging from 0.12 to 17 mg/kg (DA/egg weight). DA reduced hatching success by 40% at 0.4 mg/kg and by more than 50% at doses of 1.2 mg/kg and higher. Fifty percent of embryos treated with 1.2 mg/kg DA showed marked tonic-clonic type convulsions at 2 days post fertilization. Four days post fertilization (dpf), all embryos treated with 4.0 mg/kg DA and higher showed a complete absence of touch response reflexes. Commencing 5 dpf, rapid and constant pectoral fin movements were observed, a response which may be related to the hallmark effect in rodents of stereotypic scratching. These data indicate that zebrafish show symptoms of developmental DA toxicity as well as a similar sensitivity comparable to the effects of DA characterized in laboratory rodents.     

Domoic acid: a fascinating marine toxin

There are indications that toxic algal blooms are increasing because of pollution of coastal waters and worldwide shipping. This mini-review deals with the marine biotoxin domoic acid, also known as amnesic shellfish poison, and its main producing pennate diatom genus Pseudo-nitzschia (Bacillariophyceae). Besides contamination of seafood, these organisms have also been involved in human and marine wildlife mortality. The article aims to give an overview of all biological and environmental factors that should be considered when trying to evaluate a possible increase in toxic blooms of Pseudo-nitzschia spp. Pseudo-nitzschia blooms characteristically occur in a low light regime, at a time when the temperature is falling and at a wide range of salinities. Laboratory studies have shown that the production of domoic acid, a water-soluble amino acid, is related to silicon, phosphorus, nitrogen and trace metal (mainly iron) availability. Domoic acid has no known function in defence or primary metabolism; a role in excretion of excess photosynthetic energy or as a binding ligand for trace metals is suggested. The variability in domoic acid production by different Pseudo-nitzschia spp., or the presence of toxic and non-toxic strains of the same species, cannot be explained. The conclusion is drawn that an increase in toxic blooms of Pseudo-nitzschia spp. might be possible, especially because of the expected increase in nutrient availability from pollution and desert dust. Global warming may have an influence as well by lengthening the growth period for Pseudo-nitzschia, enlarging their global distribution and increasing the dust load through desertification.     

Ultrasensitive detection of domoic acid in mouse blood by competitive ELISA using blood collection cards.

Domoic acid (DA), an analog of the excitatory amino acid glutamate, is produced by the diatom genus Pseudo-nitzschia and acts as a neurotoxin in humans. During diatom blooms, DA can contaminate shellfish, as well as other filter feeding organisms, and can be transferred by ingestion to higher trophic levels, including marine mammals and humans. The prevalence of this algal toxin and its effects on protected species makes measurement of domoic acid in living animals a necessary biomonitoring tool for the near future. Blood collection cards have already been used for the sampling, extraction and detection of brevetoxin in blood from exposed laboratory animals and, more recently, marine mammals. However, a difficulty unique to measuring DA in blood is the rapid rate (>95% in 2h) at which it is cleared from blood. To meet this challenge, a direct competitive ELISA (cELISA), a method of detection with extremely high sensitivity and specificity, was used to analyze the blood of DA-exposed mice after extraction from the blood collection cards. More than 99% of DA was cleared from blood within 4h post dosage; however, domoic acid was still quantifiable (>0.7ngml(-1)) at 4h from blood spot extracts and still detectable at 24h when compared to control blood spots. By using this highly sensitive assay in conjunction with the use of blood spot cards for easy blood sample extraction, this method could be a very effective means of biomonitoring domoic acid in marine mammals in the field, as well as human populations.     

Effects of algal-produced neurotoxins on metabolic activity in telencephalon, optic tectum and cerebellum of Atlantic salmon (Salmo salar)

Neurotoxins from algal blooms have been reported to cause mortality in a variety of species, including sea birds, sea mammals and fish. Farmed fish cannot escape harmful algal blooms and their potential toxins, thus they are more vulnerable for exposure than wild stocks. Sublethal doses of the toxins are likely to affect fish behaviour and may impair cognitive abilities. In the present study, changes in the metabolic activity in different parts of the Atlantic salmon (Salmo salar) brain involved in central integration and cognition were investigated after exposure to sublethal doses of three algal-produced neurotoxins; saxitoxin (STX), brevetoxin (BTX) and domoic acid (DA). Fish were randomly selected to four groups for i.p. injection of saline (control) or one of the neurotoxins STX (10 microg STX/kg bw), BTX (68 microg BTX/kg bw) or DA (6 mg DA/kg bw). In addition, 14C-2-deoxyglucose was i.m. injected to measure brain metabolic activity by autoradiography. The three regions investigated were telencephalon (Tel), optic tectum (OT) and cerebellum (Ce). There were no differences in the metabolic activity after STX and BTX exposure compared to the control in these regions. However, a clear increase was observed after DA exposure. When the subregions with the highest metabolic rate were pseudocoloured in the three brain regions, the three toxins caused distinct differences in the respective patterns of metabolic activation. Fish exposed to STX displayed similar patterns as the control fish, whereas fish exposed to BTX and DA showed highest metabolic activity in subregions different from the control group. All three neurotoxins affected subregions that are believed to be involved in cognitive abilities in fish.     

The accumulation of cylindrospermopsin from the cyanobacterium Cylindrospermopsis raciborskii in tissues of the Redclaw crayfish Cherax quadricarinatus.

Redclaw crayfish, Cherax quadricarinatus harvested from an aquaculture pond infested by a bloom of the cyanobacterium Cylindrospermopsis raciborskii (order: Nostocales), were shown to accumulate the toxic alkaloid cylindrospermopsin. Pond water samples collected during the bloom contained 589 microg l(-1) of the toxin (93% in the cyanobacterial cells, 7% in the water). Crayfish from the pond contained cylindrospermopsin at concentrations of 4.3 microg g freeze dried hepatopancreas tissue and 0.9 microg g freeze dried muscle tissue. Trichomes of C. raciborskii were observed in gut contents of crayfish harvested during the cyanobacterial bloom, indicating that the most likely mechanism for accumulation of the toxin was by ingestion of cyanobacterial cells. Crayfish subjected to an extract of harvested bloom material under laboratory conditions for a period of 14 days were also found to accumulate cylindrospermopsin, indicating that this toxin is also absorbed into the tissues by direct uptake of the toxin in solution.     

Crassostrea virginica grazing on toxic and non-toxic diatoms

Despite high abundances of toxic Pseudo-nitzschia spp. over Louisiana oyster beds (Crassostrea virginica; eastern oyster) there have been no documented cases of amnesic shellfish poisoning (ASP) in the state. Two possible explanations are that oysters do not readily feed on long pointed chains of Pseudo-nitzschia cells or they discriminate against toxic cells while grazing. To test these hypotheses, short-term grazing experiments were conducted with several diatoms, including the domoic acid (DA)-producing Pseudo-nitzschia multiseries (1.31 ± 0.057 pg DA cell^?1) and the non-toxic Pseudo-nitzschia delicatissima, Thalassiosira weissflogii, and Ditylum brightwellii. Grazing rates on the small centric species T. weissflogii were significantly higher than on the larger and pointier D. brightwellii and either Pseudo-nitzschia species. Grazing on toxic P. multiseries and non-toxic P. delicatissima was not significantly different. Pseudofeces production was higher and feces production was occasionally lower in oysters fed Pseudo-nitzschia spp. than in oysters fed the other two diatoms. Our data demonstrate lower filtration rates of C. virginica on Pseudo-nitzschia spp. relative to the other diatoms tested and comparable filtration on toxic and non-toxic Pseudo-nitzschia spp. These findings suggest that eastern oysters do not discriminate amongst food types due to DA content.     

Organ distribution and bioaccumulation of microcystins in freshwater fish at different trophic levels from the eutrophic Lake Chaohu, China

This article reports the organ distribution and bioaccumulation of hepatotoxic microcystins (MCs) in freshwater fishes at different trophic levels from the large, shallow, eutrophic Lake Chaohu in September 2003, when there were heavy surface blooms of toxic cyanobacteria. Among all fish, intestines and blood had the highest average content of MC-RR + MC-LR (22.0 and 14.5 microg g(-1) DW, respectively), followed by liver, bile, and kidney (7.77, 6.32, and 5.81 microg g(-1) DW, respectively), whereas muscle had the least (1.81 microg g(-1) DW). MC content in muscle was highest in carnivorous fish (Culter ilishaeformis, 2.22 microg g(-1) DW) and omnivorous fish (Carassius auratus, 1.96 microg g(-1) DW) and was lowest in phytoplanktivorous fish (Hypophthalmichthys molitrix, 1.65 microg g(-1) DW) and herbivorous fish (Parabramis pekinensis 0.660 microg g(-1) DW). However, the amount of MC in the gut of H. molitrix (137 microg g(-1) DW) was more than 20 times that in the other fish (<6.50 microg g(-1) DW). The MCs showed a tendency to accumulate up the food chain, and piscivorous fish at the top of the food chain were at high risk of exposure to MCs in Lake Chaohu. Our study is the first to report MC concentrations in the bile and blood of wild fish. One hundred grams of fish muscle would contain 2.64-49.7 microg of MC-LR equivalent, or about 1.3-25 times the recommended tolerable daily intake of MC-LR by humans, indicating that fish are already severely contaminated by MCs and that the local authorities should warn the public of the risk of poisoning by eating the contaminated fish.