Abstract

Two different nonthermal plasma reactors at atmospheric pressure were assessed for the removal of organic micropollutants (atrazine, chlorfenvinfos, 2,4-dibromophenol, and lindane) from aqueous solutions (1–5mgL−1) at laboratory scale. Both devices were dielectric barrier discharge (DBD) reactors; one was a conventional batch reactor (R1) and the other a coaxial thin-falling-water-film reactor (R2). A first-order degradation kinetics was proposed for both experiments. The kinetic constants (k) were slightly faster in R1 (0.534min−1 for atrazine; 0.567min−1 for chlorfenvinfos; 0.802min−1 for 2,4-dibromophenol; 0.389min−1 for lindane) than in R2 (0.104min−1 for atrazine; 0.523min−1 for chlorfenvinfos; 0.273min−1 for 2,4-dibromophenol; 0.294min−1 for lindane). However, energy efficiencies were about one order of magnitude higher in R2 (89mgkW−1h−1 for atrazine; 447mgkW−1h−1 for chlorfenvinfos; 47mgkW−1h−1 for 2,4-dibromophenol; 50mgkW−1h−1 for lindane) than in R1. Degradation by-products of all four compounds were identified in R1. As expected, when the plasma treatment (R1) was applied to industrial wastewater spiked with atrazine or lindane, micropollutant removal was also achieved, although at a lower rate than with aqueous solutions (k=0.117min−1 for atrazine; k=0.061min−1 for lindane).

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