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Remediation of soils polluted with 2,4-D by electrokinetic soil flushing with facing rows of electrodes: A case study in a pilot plant

•EKSF is a feasible process for the remediation of 2,4-D polluted soils.•The rapid dissemination of 2,4-D favor the spread of pollution to environment.•A capillary barrier on the surface allows a slow transfer of water by evaporation.•2,4-D is mobilized to anode by electromigration and to cathode by...

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Bibliographic Details
Published in:Chemical engineering journal (Lausanne, Switzerland : 1996) Switzerland : 1996), 2016-02, Vol.285, p.128-136
Main Authors: Risco, C., López-Vizcaíno, R., Sáez, C., Yustres, A., Cañizares, P., Navarro, V., Rodrigo, M.A.
Format: Article
Language:English
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Summary:•EKSF is a feasible process for the remediation of 2,4-D polluted soils.•The rapid dissemination of 2,4-D favor the spread of pollution to environment.•A capillary barrier on the surface allows a slow transfer of water by evaporation.•2,4-D is mobilized to anode by electromigration and to cathode by electroosmosis.•50% of 2,4-D is removed by electrokinetic and hydraulic fluxes during EKSF. This study focuses on evaluating the application of electrokinetic soil flushing (EKSF) technologies to remediate soil polluted with 2,4-dichlorophenoxyacetic acid (2,4-D). This compound was selected as an example of polar herbicides that may cause soil percolation and groundwater contamination due to its high water solubility, lifetime and mobility. To evaluate this technology, a 40-day test was conducted on a bench-scale set-up (175dm3 of capacity) that was fully automated and operating under potentiostatic mode (1Vcm−1). The electrical current, temperature, pH, humidity and pollutant concentration in the electrolyte wells were monitored daily, and at the end of the tests, a post-analysis characterization of the soil section was performed to obtain 3-D plots of the changes in each parameter. Simultaneously, a blank test was carried out (without applying an electric field) to determine spreading of the pollutant in the soil that did not experience an electric field. The results indicate that the 2,4-D is transported to the anode wells by electromigration (the primary species is an anion under the treatment pH) and the cathode wells by electroosmotic drag, even though a lower concentration is obtained because a large volume of water is mobilized. After 40days of the EKSF treatment, 50% of the initial 2,4-D leaked into the soil was eliminated, 25% remained in the soil, and the remaining 25% was volatilized.
ISSN:1385-8947
1873-3212
DOI:10.1016/j.cej.2015.10.011