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Neurotoxicity induced in fish by domoic acid (DA) was assessed with respect to occurrence of neurotoxic signs, lethality, and histopathology by light microscopy. Sparus aurata were exposed to a single dose of DA by intraperitoneal (i.p.) injection of 0, 0.45, 0.9, and 9.0 mg DA kg(-1) bw. Mortality (66.67 ± 16.67%) was only observed in dose of 9.0 mg kg(-1) bw. Signs of neurological toxicity were detected for the doses of 0.9 and 9.0 mg DA kg(-1) bw. Furthermore, the mean concentrations (±SD) of DA detected by HPLC-UV in extracts of brain after exposure to 9.0 mg DA kg(-1) bw were 0.61 ± 0.01, 0.96 ± 0.00, and 0.36 ± 0.01 mg DA kg(-1) tissue at 1, 2, and 4 hours. The lack of major permanent brain damage in S. aurata, and reversibility of neurotoxic signs, suggest that lower susceptibility to DA or neuronal recovery occurs in affected individuals.

This article reports a light and electron microscopy investigation of the effects of Cylindrospermopsis raciborskii and Aphanizomenon ovalisporum ingestion on midgut and associated digestive diverticula of Daphnia magna. Additionally, survivorship and growth effects caused by feeding on cyanobacteria were assessed. Three cyanobacteria were used in the experiments: cylindrospermopsin (CYN)-producing C. raciborskii, CYN-producing A. ovalisporum and non-CYN-producing C. raciborskii. In order to discriminate between the alterations due to the low nutritional value of cyanobacteria and toxic effects, a control group was fed on the chlorophyte Ankistrodesmus falcatus and another control group was not fed. In the chlorophyte fed control, the epithelium lining the midgut and associated diverticula is mainly formed by strongly stained cells with an apical microvilli border. Nevertheless, unstained areas in which cell lyses had occurred were also observed. In the unfed control, the unstained areas became predominant due to an increment of cell lyses. All individuals fed on CYN-producing A. ovalisporum and some of those fed on non-CYN-producing C. raciborskii appear similar to the unfed control. However, some individuals fed on non-CYN-producing C. raciborskii showed similarities with the fed control. In contrast, the midgut and digestive diverticula of D. magna fed on CYN-producing C. raciborskii showed a widespread dissociation of epithelial cells, associated with severe intracellular disorganization, but cell lysis was less evident than in controls. These alterations cannot be attributed to CYN, because those effects were not induced by CYN-producing A. ovalisporum. Therefore, data suggest the production of another unidentified active metabolite by CYN-producing C. raciborskii, responsible for the disruption of cell adhesion in the epithelium of D. magna digestive tract. Data also show that the tested cyanobacteria are inadequate as food to D. magna, due to low nutritional value and toxic content.

We investigated the intestinal uptake and adverse effects of microcystins ingested with Microcystis on Daphnia galeata. The gut structure, blood microcystin concentration, appearance, and movements of Daphnia fed Microcystis PCC 7806 or a microcystin-deficient PCC 7806 mutant were monitored over time. Microcystins were rapidly taken up from the digestive cavity into the blood. This process apparently required a preceding disruption of the gut epithelium by an as-yet-unknown Microcystis factor. Once microcystins entered the blood, they affected the neuromuscular communication or another life function that influences major muscle systems. Consequently, the beat rates of the thoracic legs, mandibles, and second antennae as well as the activity of the foregut decreased, whereas the midgut muscles were stimulated. Finally, the animals exhibited symptoms of exhaustion and died. The present results suggest that an ingestion of between 10.2 ng and 18.3 ng of microcystin per 1 mg of Daphnia body fresh weight is sufficient to kill D. galeata within 2 d.

The effect of two strains of Cylindrospermopsis raciborskii on the survivorship, somatic growth, and detoxification processes of juvenile Daphnia magna were investigated. Both strains of C. raciborskii (and also Ankistrodesmus falcatus, used as the control) were given to newborn D. magna at equivalent biovolumes. The survival curves for D. magna subjected to the two C. raciborskii treatments differed from those of the starved and fed treatments. After 48 h of exposure, the percentage of D. magna surviving after exposure to Cylin-A (a cylindrospermopsin-producing strain isolated from Australia) and Cylin-P (a non-cylindrospermopsin-producing strain isolated from Portugal) was 10.00% and 93.33%, respectively. The strain that produces cylindrospermopsin caused the greatest toxic effect in juvenile D. magna. Statistically significant differences in D. magna body size between the four treatments (Cylin-A, Cylin-P, A. falcatus, and starved) were detected after 48 h of exposure. The juvenile D. magna that received the two C. raciborskii treatments showed an increase in size (relative to their size at T0) of 2.54% and 38.14%, respectively. These values were statistically significantly different than those of the A. falcatus–fed control (55.54%) and the starved control (11.47%). In both C. raciborskii treatments there was a tendency for increased GST enzyme activities after 24 h of exposure. Cylindrospermopsin was detected (HPLC-MS/MS) in D. magna tissues after 24 and 48 h (0.025 and 0.02 ng animal−1, respectively). The results of this study indicate that C. raciborskii can affect the fitness and growth potential of juvenile D. magna. © 2004 Wiley Periodicals, Inc. Environ Toxicol 19: 453–459, 2004.

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.

The freshwater cyanobacterium Cylindrospermopsis raciborskii has become increasingly prevalent in freshwaters worldwide. This species is a concern from a water quality perspective due to its known ability to produce a potent hepatotoxic alkaloid cylindrospermopsin, which has been implicated in outbreaks of human sickness and cattle mortality. C. raciborskii strains isolated from Brazil have also been found to produce the highly toxic paralytic shellfish poisons (PSPs). This article reports the toxicity of four strains of C. raciborskii taken from three reservoirs and one river in Portugal, as well as the occurrence of this species in other water bodies used for potable and recreational purposes. All four strains grown in pure culture in the laboratory were found to be toxic in the mouse bioassay at 8–24 h after intraperitoneal administration of single doses ranging from 1337 to 1572 mg kg −1 Histological examination indicated that liver damage was the primary lesion; in addition, there was inflammation in the intestine. HPLC/MS tests for the presence of cylindrospermopsin, microcystins, and PSP toxins were negative. The available evidence suggests that another toxin may be present. This constitutes the first report of toxic C. raciborskii in Europe and draws attention to the need for increased monitoring of this cyanobacterium in water bodies used for potable and recreational purposes.