Remediation of Atrazine-contaminated Soil and Water by Nano Zerovalent Iron

Satapanajaru, T.; Anurakpongsatorn, P.; Pengthamkeerati, P.; Boparai, H.

Remediation of Atrazine-contaminated Soil and Water by Nano Zerovalent Iron

2008

Satapanajaru, T. | Anurakpongsatorn, P. | Pengthamkeerati, P. | Boparai, H.

Atrazine-contaminated soil may require remediation to mitigate ground and surface water contamination. We determined the effectiveness of nano zerovalent iron (nano ZVI) to dechlorinate atrazine (2-chloro-4ethylamino-6-iso-propylamino-1,3,5-triazine) in contaminated water and soil. This study determined the effects of iron sources, solution pH, Pd catalyst and presence of Fe or Al sulfate salts on the destruction of atrazine in water and soil. Our results indicate nano ZVI can be successfully used to remediate atrazine in water and soil. Aqueous solution of atrazine (30 mg l⁻¹) was treated with 2% (w/v) of nano ZVI and 5% (w/v) of commercial ZVI. Although, iron dose in nano ZVI treatment was less than that in commercial ZVI treatment, atrazine destruction kinetic rate (k obs) of nano ZVI treatment (1.39 days⁻¹) was around seven times higher than that of commercial ZVI treatment (0.18 days⁻¹). Reductive dechlorination was the major process in destruction of atrazine by nano ZVI. The dechlorination product was 2-ethyl-amino-4-isopropylamino-1,3,5-triazine. Lowering the pH from 9 to 4 increased the destruction kinetic rates of atrazine by nano ZVI. Moreover, nano ZVI/Pd enhanced destruction kinetic rates of atrazine (3.36 day⁻¹). Pd played the important role as a catalyst during treatment of atrazine by nano ZVI. Atrazine destruction kinetic rates were greatly enhanced in both contaminated water and soil treatments by nano ZVI when sulfate salts of Fe(II), Fe(III) or Al(III) was add with the following order of removal rates: Al (III) (2.23 day⁻¹) > Fe (III) (2.04 day⁻¹) > Fe(II) (1.79 day⁻¹). The same results were found in atrazine-nano ZVI-soil incubation experiments.

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