microcystin-yr and nodularin

Microcystins (MCs) are a growing problem in drinking water supplies worldwide. Common analytical techniques used to determine MC concentrations have several shortcomings, including extensive sample handling and lengthy analysis times. A simple, rapid method for quantitation of MCs by matrix-assisted laser desorption ionization time-of-flight mass spectrometry (MALDI-TOF MS) is presented. Four potential internal standards were tested, including an 15N-labeled MC. For MC-LR in mixed standard solutions, a linear range of 0.11-5.0 microM (R2 = 0.98) was achieved, with a method detection limit (MDL) of 0.015 microM. Matrix effects due to extracted cell components decreased the MC-LR linear range slightly to 0.19-5.0 microM (R2 = 0.99), with MDL = 0.058 microM. Extensive analysis of possible internal standards indicates that nodularin was preferred over [15N]10-microcystin-YR or angiotensin I. The ionization efficiency and analyte-analyte suppression for four MCs of varying polarity are presented; the three polar congeners exhibited good ionization efficiency and acceptable levels of analyte-analyte suppression. These results indicate that MALDI-TOF MS represents a viable alternative for the quantitative measurement of MCs in field samples.

Topics: Angiotensin I; Bacterial Toxins; Cyanobacteria Toxins; Marine Toxins; Microcystins; Nitrogen Isotopes; Peptides, Cyclic; Reproducibility of Results; Sensitivity and Specificity; Spectrometry, Mass, Matrix-Assisted Laser Desorption-Ionization; Water Microbiology; Water Supply

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

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