Advanced oxidation processes coupled with electrocoagulation for the exhaustive abatement of Cr-EDTA

Using Cr-EDTA as a model system, a two-step method has been investigated for the abatement of persistent chromium complexes in water. The treatment consists of an oxidative decomposition of the organic ligands by means of ozonization or electrochemical oxidation at a boron doped diamond (BDD) electr...

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Published inWater research (Oxford) Vol. 45; no. 5; pp. 2122 - 2130
Main Authors Durante, Christian, Cuscov, Marco, Isse, Abdirisak Ahmed, Sandonà, Giancarlo, Gennaro, Armando
Format Journal Article
LanguageEnglish
Published Kidlington Elsevier Ltd 01.02.2011
Elsevier
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Summary:Using Cr-EDTA as a model system, a two-step method has been investigated for the abatement of persistent chromium complexes in water. The treatment consists of an oxidative decomposition of the organic ligands by means of ozonization or electrochemical oxidation at a boron doped diamond (BDD) electrode, followed by removal of the metal via electrochemical coagulation. In the designed synthetic waste, EDTA has been used both as a chelating agent and as a mimic of the organic content of a typical wastewater provided by a purification leather plant. A crucial point evaluated is the influence of the oxidative pretreatment on the chemical modification of the synthetic waste and hence on the electrocoagulation efficacy. Because of the great stability of Cr complexes, such as Cr-EDTA, the classical coagulation methods, based on ligand exchange between Cr(III) and Fe(II) or Fe(III), are ineffective toward Cr abatement in the presence of organic substances. On the contrary, when advanced oxidation processes (AOPs), such as ozonization or electrooxidation at a BDD anode are applied in series with electrocoagulation (EC), complete abatement of the recalcitrant Cr fraction can be achieved. ECs have been carried out by using Fe sacrificial anodes, with alternating polarization and complete Cr abatement (over 99%) has been obtained with modest charge consumption. It has been found that Cr(III) is first oxidized to Cr(VI) in the AOP preceding EC. Then, during EC, Cr(VI) is mainly reduced back to Cr(III) by electrogenerated Fe(II). Thus, Cr is mainly eliminated as Cr(III). However, a small fraction of Cr(VI) goes with the precipitate as confirmed by XPS analysis of the sludge. ► Conventional methods of heavy metal removal from wastewaters are inefficient in the abatement of recalcitrant Cr fractions. ► In this paper, a two-step method is shown to be efficient in the complete abatement of Cr-EDTA. ► The organic component is first destroyed by either ozonization or electrooxidation. ► Then, the free Cr ions are removed by electrocoagulation on Fe anodes. ► Decomplexation of Cr is shown to be fundamental for the success of the method.
Bibliography:http://dx.doi.org/10.1016/j.watres.2010.12.022
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ISSN:0043-1354
1879-2448
DOI:10.1016/j.watres.2010.12.022