Method for detecting classes of microcystins by combination of protein phosphatase inhibition assay and ELISA: comparison with LC-MS.
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.
Mountfort
Douglas O
DO
Cawthron Institute, Private Bag 2, Nelson, New Zealand. douglas.mountfort@cawthron.org.nz
Holland
Patrick
P
Sprosen
Jan
J
D001427:Bacterial Toxins / Q000032:analysis* / Q000145:classification / Q000633:toxicity; D002853:Chromatography, Liquid / Q000379:methods; D000458:Cyanobacteria / Q000737:chemistry; D004797:Enzyme-Linked Immunosorbent Assay; D008387:Marine Toxins; D013058:Mass Spectrometry / Q000379:methods; D052998:Microcystins; D010456:Peptides, Cyclic / Q000032:analysis; D010749:Phosphoprotein Phosphatases / Q000037:antagonists & inhibitors* / Q000737:chemistry; D014873:Water Pollutants / Q000032:analysis
D001427:Bacterial Toxins; D008387:Marine Toxins; D052998:Microcystins; D010456:Peptides, Cyclic; D014873:Water Pollutants; C063998:nodularin; C065685:microcystin YR; C063855:microcystin RR; D010749:Phosphoprotein Phosphatases; C057862:cyanoginosin LR