microcystin-rr and nodularin

An analytical procedure is proposed for determining three cyanotoxins (microcystin RR, microcystin LR, and nodularin) and two phycotoxins (domoic and okadaic acids) in seawater and algae-based food supplements. The toxins were first isolated by a salting out liquid extraction procedure. Since the concentration expected in the samples was very low, a dispersive liquid-liquid microextraction procedure was included for preconcentration. The ionic liquid 1-hexyl-3-methylimidazolium hexafluorophosphate (80 mg) was used as green extractant solvent and acetonitrile as disperser solvent (0.5 mL) for a 10 mL sample volume at pH 1.5, following the principles of green analytical chemistry. Liquid chromatography with electrospray ionization and quadrupole time of flight-mass spectrometry (LC-Q-TOF-MS) was used. The selectivity of the detection system, based on accurate mass measurements, allowed the toxins to be unequivocally identified. Mass spectra for quadrupole time of flight-mass spectrometry (Q-TOF-MS) and Q-TOF-MS/MS were recorded in the positive ion mode and quantification was based on the protonated molecule. Retention times ranged between 6.2 and 17.9 min using a mobile phase composed by a mixture of methanol and formic acid (0.1%). None of the target toxins were detected in any of the seawater samples analyzed, above their corresponding detection limits. However, microcystin LR was detected in the blue green alga sample.

Topics: Acetonitriles; Borates; Chromatography, High Pressure Liquid; Dietary Supplements; Food Contamination; Imidazoles; Ionic Liquids; Kainic Acid; Liquid Phase Microextraction; Marine Toxins; Microcystins; Okadaic Acid; Peptides, Cyclic; Seawater; Solvents; Spain; Spirulina; Stramenopiles; Tandem Mass Spectrometry

Monitoring the quality of freshwater is an important issue for public health. In the context of the European project μAqua, 150 samples were collected from several waters in France, Germany, Ireland, Italy, and Turkey for 2 yr. These samples were analyzed using 2 multitoxin detection methods previously developed: a microsphere-based method coupled to flow-cytometry, and an ultra-performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS) method. The presence of microcystins, nodularin, domoic acid, cylindrospermopsin, and several analogues of anatoxin-a (ATX-a) was monitored. No traces of cylindrospermopsin or domoic acid were found in any of the environmental samples. Microcystin-LR and microcystin-RR were detected in 2 samples from Turkey and Germany. In the case of ATX-a derivatives, 75% of samples contained mainly H

Topics: Alkaloids; Bacterial Toxins; Bridged Bicyclo Compounds, Heterocyclic; Chromatography, Liquid; Cyanobacteria; Cyanobacteria Toxins; Environmental Monitoring; Eutrophication; Flow Cytometry; France; Fresh Water; Germany; Italy; Limit of Detection; Marine Toxins; Microcystins; Molecular Structure; Peptides, Cyclic; Tandem Mass Spectrometry; Tropanes; Turkey; Uracil; Water Pollutants, Chemical

In countries around the Baltic Sea grazing ruminants have access to and drink, surface water from lakes, rivers and in several coastal regions. The water quality of these naturally occurring reservoirs affects performance and health of livestock. In the Baltic Sea both microcystin (MC) and nodularin (NOD) occurs as cyclic peptides and have hepatotoxic effects. Although cattle obviously have died after consuming contaminated water very little information is available as to how susceptible ruminants are to the toxins produced by cyanobacteria. The critical question as to whether the rumen microflora might constitute a protective shield is unresolved. For this reason our aim is to investigate a possible degradation rate of these toxins in rumen.. The ability of rumen microorganisms to degrade certain important cyanotoxins (MC-LR, YR, RR and NOD) was studied in vitro by incubating with rumen fluid at three different concentrations (0.05, 0.5 and 5 μg/mL) for 3 h. The degradation efficiencies were determined by LC-MS (ESI) positive mode. Degradation was observed in the following order MC-RR 36%, NOD 35%, MC-RR 25% and MC-LR 8.9% at lower concentrations within 3 h. However, average degradation was observed at concentration of 0.5 μg/mL. No degradation was observed in higher concentrations for entire 3 h. The present results reveal that the degradation was both dose and time dependent.. In conclusion the present results suggest that the rumen microbial flora may protect ruminants from being intoxicated by Cyanotoxins.

Topics: Animals; Body Fluids; Cattle; Female; Marine Toxins; Microcystins; Peptides, Cyclic; Rumen

Depending on the class of microcystin the protein phosphatase inhibition assay shows different sensitivities to different classes of toxin. We have determined that the IC50 values obtained from dose-response curves for the inhibition of the enzyme by micro-cystin LR, nodularin, YR, and RR were 2.2, 1.8, 9 and 175 nM, respectively. When equimolar amounts of these toxins were determined by the ELISA assay with microcystin LR as the standard, the assay showed equivalence in toxin responses. However, when the toxins were determined by the protein phosphatase inhibition assay using microcystin LR as the standard, the ratios of the values determined by PP-2A to ELISA decreased in the order: nodularin (2.23) microcystin LR (1.1)> microcystin YR (0.63)> microcystin RR (0.06). When the ratios for each standard were plotted against the IC50 values, the log-log plot was negative linear, and the lowest value for the IC50 corresponded with the lowest ratio. The differential sensitivity of the PP-2A assay to the various standards was used to establish an indicative toxicity ranking (ITR) where a ranking of 1 (the highest) was assigned to ratios of > or = 0.8 or greater, and 3 (the lowest) to values < or = 0.2. The three ranking classes corresponded to toxin equivalence represented by the four standards. The new method allows not only the determination of microcystin toxins in terms of stoichiometry (ELISA) but also in terms of indicative toxicity. The method can be performed using the same instrument (e.g. multiwell fluorimeter with absorbance capability) and offers an advantage to methods presently used to determine microcystins (e.g. ELISA or LC-MS). The former has the propensity to overestimate toxicity because it measures equivalence to microcystin LR and is a stoichiometric measurement and the latter has the disadvantage in that relatively few of the microcystins that occur naturally are available as standards. The new method was applied to the analysis of sample from lakes and streams from temperate locations and to extracts of cyanobacterial mats from ponds and streams in cold temperature locations.

Topics: Bacterial Toxins; Chromatography, Liquid; Cyanobacteria; Enzyme-Linked Immunosorbent Assay; Marine Toxins; Mass Spectrometry; Microcystins; Peptides, Cyclic; Phosphoprotein Phosphatases; Water Pollutants

Cyanobacteria (blue-green algae) (e.g., Microcystis and Nodularia spp.) capable of producing toxic peptides are found in fresh and brackish water worldwide. These toxins include the microcystin (MC) heptapeptides (>60 congeners) and the nodularin pentapeptides (ca. 5 congeners). Cyanobacterial cyclic peptide toxins are harmful to man, other mammals, birds, and fish. Acute exposure to high concentrations of these toxins causes liver damage, while subchronic or chronic exposure may promote liver tumor formation. The detection of cyclic peptide cyanobacterial toxins in surface and drinking waters has been hampered by the low limits of detection required and that the present routine detection is restricted to a few of the congeners. The unusual beta-amino acid ADDA (4E,6E-3-amino-9-methoxy-2,6,8-trimethyl-10-phenyldeca-4,6-dienoic acid) is present in most (>80%) of the known toxic penta- and heptapeptide toxin congeners. Here, we report the synthesis of two ADDA-haptens, the raising of antibodies to ADDA, and the development of a competitive indirect ELISA for the detection of microcystins and nodularins utilizing these antibodies. The assay has a limit of quantitation of 0.02-0.07 ng/mL (depending on which congeners are present), lower than the WHO-proposed guideline (1 ng/mL) for drinking water, irrespective of the sample matrix (raw water, drinking water, or pure toxin in PBS). This new ELISA is robust, can be performed without sample preconcentration, detects toxins in freshwater samples at lower concentrations than does the protein phosphatase inhibition assay, and shows very good cross-reactivity with all cyanobacterial cyclic peptide toxin congeners tested to date (MC-LR, -RR, -YR, -LW, -LF, 3-desmethyl-MC-LR, 3-desmethyl-MC-RR, and nodularin).

Topics: Cyanobacteria; Immunoassay; Marine Toxins; Microcystins; Peptides, Cyclic; Water Pollutants; Water Pollution

Topics: Chromatography, High Pressure Liquid; Cyanobacteria; Marine Toxins; Microcystins; Peptides, Cyclic

Three microcystins, YR, LR and RR and nodularin, all of which are hepatotoxic compounds, inhibited dose-dependently the activity of protein phosphatase 2A in and the specific [3H]okadaic acid binding to a cytosolic fraction of mouse skin, as strongly as okadaic acid. However, microcytins and nodularin did not induce any effects on mouse skin or primary human fibroblasts. Microinjection of microcystin YR into primary human fibroblasts induced morphological changes which were induced by incubation with okadaic acid. Microcystins and nodularin penetrate into the epithelial cells of mouse skin and human fibroblasts with difficulty, which reflects tissue specificity of the compounds.

Topics: Animals; Cells, Cultured; Cytosol; Ethers, Cyclic; Fibroblasts; Humans; Marine Toxins; Mice; Microcystins; Okadaic Acid; Peptides, Cyclic; Phosphoprotein Phosphatases; Plants, Toxic; Protein Binding; Protein Phosphatase 2; Skin

Microcystins and nodularin, isolated from toxic blue-green algae, are hepatotoxic monocyclic polypeptides. Both microcystins and nodularin inhibited in vitro protein phosphatase activity present in a cytosolic fraction of mouse liver, bound to the okadaic acid receptors, protein phosphatases 1 and 2A, and thus resulted in the increase of phosphoproteins; this was referred to as the apparent "activation" of protein kinases. Their concentrations causing 50% of the maximal effects are comparable to that of okadaic acid, a potent protein phosphatase inhibitor and a potent tumor promoter, in the nanomolar range of concentration. The increase of phosphoproteins was observed in rat primary cultured hepatocytes and was subsequently associated with morphological changes, which appeared to be a step in the process of hepatotoxicity. The well-known hepatotoxic compounds, alpha-amanitin and phalloidin, did not show any effects similar to those of microcystins, nodularin and okadaic acid. It is suggested that the hepatotoxicity of microcystins and nodularin may result from inhibition of protein phosphatases and the increase of phosphoproteins.

Topics: Animals; Cells, Cultured; Cyanobacteria; Ethers, Cyclic; Liver; Male; Marine Toxins; Mice; Microcystins; Okadaic Acid; Peptides, Cyclic; Phosphoprotein Phosphatases; Phosphoproteins; Protein Kinases; Rats; Rats, Inbred Strains

The cyclic peptide hepatotoxins microcystin-LR, 7-desmethyl-microcystin-RR and nodularin are potent inhibitors of the protein phosphatases type 1 and type 2A. Their potency of inhibition resembles calyculin-A and to a lesser extent okadaic acid. These hepatotoxins increase the overall level of protein phosphorylation in hepatocytes. Evidence is presented to indicate that in hepatocytes the morphological changes and effects on the cytoskeleton are due to phosphatase inhibition. The potency of these compounds in inducing hepatocyte deformation is similar to their potency in inhibiting phosphatase activity. These results suggest that the hepatotoxicity of these peptides is related to inhibition of phosphatases, and further indicate the importance of the protein phosphorylation in maintenance of structural and homeostatic integrity in these cells.

Topics: Amino Acid Sequence; Animals; Carrier Proteins; Chickens; Cyanobacteria; Enzyme Inhibitors; Intracellular Signaling Peptides and Proteins; Liver; Marine Toxins; Microcystins; Molecular Sequence Data; Peptides, Cyclic; Phosphoprotein Phosphatases; Phosphorylation; Proteins