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¾Í·ÒëһϽáÂÛ²¿·Ö¾ÍÐÐÁË 4. Conclusions It has been demonstrated that anodic oxidation, electro-Fenton and photoelectro-Fenton with a BDD anode are viable methods to decontaminate acidic wastewaters containing 2,4-DP. These electrochemical techniques yield overall mineralization at high current due to the great production of oxidant BDD(OH) favoring the destruction of final carboxylic acids. OH formed from Fenton¡¯s reaction (3) destroys more rapidly aromatic products, thus making the electro-Fenton and photoelectro-Fenton processes much more efficient than anodic oxidation. UVA light in photoelectro-Fenton with BDD has little in?uence on the degradation rate of pollutants. The alternative use of a Ptanode in the same methods under comparable conditions leads to slower decontamination because of the lower oxidizing power of Pt(OH). The increase in current accelerates the degradation of all pollutants, but with the consumption of more speci?c charge. The initial chlorine is released as Cl2, which is stable in the treatments with Pt and oxidized to Cl2 at the BDD anode. The 2,4-DP decay always follows a pseudo-?rst-order kinetics. Chlorohydroquinone and chloro-p-benzoquinone are detected as aromatic intermediates and maleic, fumaric, malic, lactic, pyruvic, acetic, formic and oxalic acids are identi?ed as carboxylic acids. Acetic acid is destroyed by the oxidant BDD(OH), but not by Pt(OH). Oxalic acid and Fe3+ -oxa-lato complexes are also converted into CO2 by BDD(OH), whereas the latter complexes are simultaneously photodecarboxylated under UVA irradiation in photoelectro-Fenton. |
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