Kinetic studies of the AOP radical-based oxidative and reductive destruction of pesticides and model compounds in water.

ABSTRACT

Absolute second-order rate constants for hydroxyl radical (HO) reaction with four organophosphorus pesticides, malathion, parathion, fenthion and ethion, and a suite of model compounds of structure (EtO)2P(S)-X (where X = Cl, F, SH, SEt, OCH2CF3, OEt, NH2, and CH3) were measured using electron pulse radiolysis and transient absorption techniques. Specific values were determined for these four pesticides as k = (3.89 ±â€¯0.28) x 109, (2.20 ±â€¯0.15) x 109, (2.02 ±â€¯0.15) x 109 and (2.93 ±â€¯0.10) x 109 M-1 s-1, respectively, at 20 ±â€¯2 °C. The corresponding Brönsted plot for all these compounds demonstrated that the HO oxidation reaction mechanism for the pesticides was consistent with the model compounds, attributed to initial HO-adduct formation at the P(S) moiety. For malathion, steady-state 60Co radiolysis and 31P NMR analyses showed that hydroxyl radical-induced oxidation produces the far more potent isomalathion, but only with an efficiency of 4.9 ±â€¯0.3%. Analogous kinetic measurements for the hydrated electron induced reduction of these pesticides gave specific rate constants of k = (3.38 ±â€¯0.14) x 109, (1.38 ±â€¯0.10) x 109, (1.19 ±â€¯0.12) x 109 and (1.20 ±â€¯0.06) x 109 M-1 s-1, respectively, for malathion, parathion, fenthion and ethion. Model compound measurements again supported a single reduction reaction mechanism, proposed to be electron addition at the PS bond to form the radical anion. These results demonstrate, for the first time, that the radical-based treatment of organophosphorus contaminated waters may present a potential toxicological risk if advanced oxidative processes are used.