Application of surface complexation modeling to the reactivity of iron(II) with nitroaromatic and oxime carbamate contaminants in aqueous TiO2 suspensions

This study reports on the application of surface complexation modeling to interpret observed kinetic trends for Fe(II) redox reactions with model nitroaromatic (4-chloronitrobenzene) and oxime carbamate (oxamyl) contaminants in aqueous TiO(2(s)) suspensions. Pseudo-first-order rate constants for reduction of the two probe contaminants (k(red), s(-1)) vary by several orders of magnitude with changing conditions (100-500 microM Fe(II), 0-15 g L(-1) TiO(2(s)), pH 2-9), but the relationship between reaction rates and Fe(II) speciation differs considerably for the two contaminants. For oxamyl, k(red) measurements are most strongly correlated with the volumetric total adsorbed Fe(II) concentration (moles Fe(II) adsorbed per liter of TiO(2(s)) suspension), whereas k(red) measurements for 4-chloronitrobenzene are proportional to the concentration of the hydrolyzed Fe(II) surface complex (equivalent TiOFe(II)OH(0)). The differing trends demonstrate that Fe(II) redox reactivity at the aqueous/TiO(2(s)) interface is influenced, in part, by specific molecular interactions with the target oxidant. Results are also geochemically relevant in that they demonstrate unambiguously that mononuclear Fe(II)-metal (hydr)oxide surface complexes are sufficiently reactive species to reduce nitroaromatic contaminants, an issue that remained open following earlier studies in Fe(III) (hydr)oxide suspensions because structural Fe(II) species are simultaneously present in such systems because of interfacial Fe(II)-to-Fe(III) electron transfer processes that occur on Fe(II) adsorption.