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Dep. of Soil and Water, The Connecticut Agric. Exp. Stn., P.O. Box 1106, New Haven, CT 06504;
Institüt für Bodenkunde und Standortslehre, Bodenchemie (Nr. 310), Universität Hohenheim, 7000 Stuttgart 70, Federal Republic of Germany.
* Corresponding author.
ABSTRACT
Fenton-type reactions of hydrogen peroxide with Fe compounds generate hydroxyl radical (OH-) or other reactive species and are potentially useful for degrading organic contaminants in soil. The use of simple Fe salts is limited, however. This study investigated certain pH 6-soluble Fe(III) complexes (Fe-L, where L is an organic ligand) as catalysts for degradation of herbicides 2,4-dichlorophenoxyacetic acid (2,4-D) and metolachor (2-chloro-N-[2-ethyl-6-methylphenyl]-N-[2-methoxy-1-methylethyl]acetamide). Reactions were carried out in 1:1 aqueous suspensions of a topsoil (15.7 g kg–1 organic C) at the natural pH of 5.7 with herbicides at concentrations representative of a spill (2–3 g kg–1, about 0.01 mol kg–1). The two herbicides had contrasting sorption behavior in that 2,4-D was mostly in solution, whereas metolachlor was mostly sorbed. The best results were obtained using Fe-nitrilotriacetate (NTA) or Fehydroxyethyleniminodiacetate (HEIDA) at 0.01 mol kg–1 and [H2O2]
0.5 mol kg–1. The gallic acid complex was less effective. In 3 h, 14C-labeled 2,4-D was quantitatively dechlorinated and partially (15–30%) converted to 14CO2: metolachlor was 93% transformed and 29% dechlorinated. Controls using free ligand plus peroxide or peroxide alone gave little or no reaction. Fe-L + H2O2 was superior to the Fenton reagent itself (Fe2+ + H2O2). The results of this study demonstrate that relatively mild chemical oxidation can be effective for remediation of certain contaminants in soil.
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