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ion is not feasible because localized carbon centered radicals do not absorb wavelength within the range of our detection system. With this in mind, SCNcompetition kinetics were employed for determination of the overall bimolecular rate constant for •OH and MCHM. The competition kinetics was obtained by monitoring a characteristic absorption of (SCN)2-• at 470 nm as described earlier. A decrease in the absorbance of (SCN)2-• at 472 nm is observed with increasing MCHM added in the

Advanced Oxidation Processes of Problematic Toxin and Water Contaminants: Cylindrospermopsin, Iopamidol, 4-methylcyclohexane Methanol and Propylene Glycol Phenyl Ether